Processing biomass

ABSTRACT

Biomass (e.g., plant biomass, animal biomass, and municipal waste biomass) is processed to produce useful products, such as fuels. For example, systems can use feedstock materials, such as cellulosic and/or lignocellulosic materials, to produce ethanol and/or butanol, e.g., by fermentation.

RELATED APPLICATIONS

This application claims priority from U.S. Provisional Application Ser. No. 61/049,407, filed Apr. 30, 2008, the full disclosure of which is incorporated by reference herein.

All other patents, patent applications and publications referenced herein or attached hereto as Appendices A to E are incorporated herein by reference in their entireties.

TECHNICAL FIELD

This invention relates to processing biomass, and products made therefrom.

BACKGROUND

Various carbohydrates, such as cellulosic and lignocellulosic materials, e.g., in fibrous form, are produced, processed, and used in large quantities in a number of applications. Often such materials are used once, and then discarded as waste, or are simply considered to be waste materials, e.g., sewage, bagasse, sawdust, and stover.

Various cellulosic and lignocellulosic materials, their uses, and applications have been described in U.S. Pat. Nos. 7,307,108, 7,074,918, 6,448,307, 6,258,876, 6,207,729, 5,973,035 and 5,952,105; and in various patent applications, including “FIBROUS MATERIALS AND COMPOSITES,” PCT/US2006/010648, filed on Mar. 23, 2006, and “FIBROUS MATERIALS AND COMPOSITES,” U.S. patent application Publication No. 2007/0045456.

SUMMARY

Generally, the inventions described herein relate to carbohydrate-containing materials (e.g., biomass materials or biomass-derived materials, such as starchy materials, cellulosic materials, lignocellulosic materials, or biomass materials that are or that include significant amounts of low molecular weight sugars (e.g., monosaccharides, disaccharides or trisaccharides), methods of making and processing such materials to change their structure, e.g., functionalize these materials with one or more desired types and amounts of functional groups, and products made from the structurally changed materials. For example, many of the methods described herein can provide cellulosic and/or lignocellulosic materials that have a lower molecular weight and/or crystallinity relative to a native material. Many of the methods provide materials that can be more readily utilized by a variety of microorganisms to produce useful products, such as hydrogen, alcohols (e.g., ethanol or butanol), organic acids (e.g., acetic acid), hydrocarbons, co-products (e.g., proteins) or mixtures of any of these.

In some instances, functionalized biomass is more soluble and more readily utilized by microorganisms in comparison to biomass that has not been functionalized. In addition, many of the functionalized materials described herein are less prone to oxidation and can have enhanced long-term stability (e.g., oxidation in air under ambient conditions). Many of the products obtained, such as ethanol or n-butanol, can be utilized as a fuel for powering cars, trucks, tractors, ships or trains, e.g., as an internal combustion fuel or as a fuel cell feedstock. Many of the products obtained can also be utilized to power aircraft, such as planes, e.g., having jet engines or helicopters. In addition, the products described herein can be utilized for electrical power generation, e.g., in a conventional steam generating plant or in a fuel cell plant.

In one aspect, the invention features a method that includes converting a low molecular weight sugar, or a material that includes a low molecular weight sugar, in a mixture with a biomass, a microorganism, and a solvent or a solvent system, e.g., water or a mixture of water and an organic solvent, to a product. Examples of solvents or solvent systems include water, hexane, hexadecane, glycerol, chloroform, toluene, ethyl acetate, petroleum ether, liquefied petroleum gas (LPG), ionic liquids and mixtures thereof. The solvent or solvent system can be in the form of a single phase or two or more phases. The biomass can be, e.g., in fibrous form.

In some instances, having a biomass material (e.g., treated by any method described herein or untreated) present during production of a product, such as ethanol, can enhance the production rate of the product. Without wishing to be bound by any particular theory, it is believed that having a solid present, such as a high surface area and/or high porosity solid, can increase reaction rates by increasing the effective concentration of solutes and providing a substrate on which reactions can occur. For example, an irradiated or an un-irradiated biomass material, e.g., a paper fiber, can be added to a fermentation process, such as during a corn-ethanol fermentation or a sugarcane extract fermentation, to increase the rate of production by 10, 15, 20, 30, 40, 50, 75, 100 percent or more, e.g., 150 percent. The biomass material can have a high surface area, high porosity, and/or low bulk density. In some embodiments, the biomass is present in the mixture from about 0.5 percent to about 50 percent by weight, such as between about 1 percent and about 25 percent by weight, or between about 2 percent and about 12.5 percent by weight. In other embodiments, the biomass is present in amounts greater than about 0.5 percent by weight, such as greater than about 1, 2, 3, 4, 5, 6, 7, 8, 9, or even greater than about 10 percent by weight. For example, in some embodiments, an oxidized, sonicated, steam exploded and/or pyrolyzed biomass material, such as a paper or cotton fiber, can be added to a low molecular weight sugar fermentation process, e.g., to enhance fermentation rate and output.

Some implementations include one or more of the following features.

The biomass may comprise a fibrous material. Converting can include allowing the microorganism to convert at least a portion of the low molecular weight sugar to ethanol. Form example, converting can comprise fermentation. The microorganism can comprise a yeast, e.g., selected from the group consisting of S. cerevisiae and P. stipitis, or a bacterium such as Zymomonas mobilis. Converting can exhibit a % performance is at least 140%, in some cases at least 170%.

The method can further include irradiating the fibrous biomass prior to mixing, e.g., with ionizing radiation, for example at a total dosage of at least 5 Mrad. Irradiating can be performed using a particle beam. Irradiating can be conducted under conditions selected to reduce the molecular weight of the biomass.

The biomass can have a bulk density of less than about 0.5 g/cm³. The biomass can have a BET surface area of greater than 0.25 m²/g, and/or a length to diameter ratio of at least 5. The biomass can have a porosity greater than 50%.

The method can further include physically preparing the biomass, e.g., by shearing, or by reducing the size of the biomass by stone grinding, mechanical ripping or tearing, pin grinding, or air attrition milling. The biomass can have internal fibers, and can have been sheared to an extent that its internal fibers are substantially exposed.

The biomass may be or include a cellulosic or lignocellulosic material. For example, the biomass can be selected from the group consisting of paper, paper products, paper waste, wood, particle board, sawdust, agricultural waste, sewage, silage, grasses, rice hulls, bagasse, cotton, jute, hemp, flax, bamboo, sisal, abaca, straw, corn cobs, corn stover, switchgrass, alfalfa, hay, rice hulls, coconut hair, cotton, seaweed, algae, and mixtures thereof.

The method may further include subjecting the biomass to enzymatic hydrolysis, and in some cases converting the hydrolyzed material to the product.

In another aspect, the invention features a method for dissolving a cellulosic or lignocellulosic material, the method comprising combining a cellulosic or lignocellulosic material with a solvent system comprising DMSO and a salt.

Solvent systems for cellulosic and lignocellulosic materials include DMSO-salt systems. Such systems include, for example, DMSO in combination with a lithium, magnesium, potassium, sodium or zinc salt. Lithium salts include LiCl, LiBr, LiI, lithium perchlorate and lithium nitrate. Magnesium salts include magnesium nitrate and magnesium chloride. Potassium salts include potassium iodide and nitrate. Examples of sodium salts include sodium iodide and nitrate. Examples of zinc salts include zinc chloride and nitrate. Any salt can be anhydrous or hydrated. Typical loadings of the salt in the DMSO are between about 1 and about 50 percent, e.g., between about 2 and 25, between about 3 and 15 or between about 4 and 12.5 percent by weight.

In other implementations, the salt can be a fluoride salt, e.g. tetrabutyl ammonium fluoride. The method can further include irradiating the cellulosic or lignocellulosic material. The cellulosic or lignocellulosic material can be selected from the group consisting of paper, paper products, paper waste, wood, particle board, sawdust, agricultural waste, sewage, silage, grasses, rice hulls, bagasse, cotton, jute, hemp, flax, bamboo, sisal, abaca, straw, corn cobs, corn stover, switchgrass, alfalfa, hay, rice hulls, coconut hair, cotton, seaweed, algae, and mixtures thereof. In some cases, the cellulosic or lignocellulosic material has a bulk density of less than about 0.5 g/cm³ (prior to addition to the solvent system) and a porosity of at least 50%.

Materials are disclosed herein that include a plurality of saccharide units arranged in a molecular chain, wherein from about 1 out of every 2 to about 1 out of every 250 saccharide units includes a carboxylic acid group, or an ester or salt thereof. In another aspect, materials include a plurality of such molecular chains. For example, about 1 out of every 8, 1 out of every 10, 1 out of every 50, or 1 out of every 100 saccharide units of each chain can include a carboxylic acid group, or an ester or salt thereof. In some embodiments, the saccharide units can include 5 or 6 carbon saccharide units. Each chain can have between about 10 and about 200 saccharide units, e.g., between about 10 and about 100 or between about 10 and about 50. For example, each chain can include hemicellulose or cellulose. In some embodiments, each chain also includes saccharide units that include nitroso, nitro, or nitrile groups.

In some embodiments, the average molecular weight of the materials relative to PEG standards can be from about 1,000 to about 1,000,000, such as between 1,500 and 200,000 or 2,000 and 10,000. For example, the average molecular weight of the materials relative to PEG standards can be less than about 10,000.

Methods of changing a molecular and/or a supramolecular structure of a biomass feedstock are disclosed herein that include 1) irradiating the biomass feedstock with radiation, such as photons, electrons or ions of sufficient energy to ionize the biomass feedstock, to provide a first level of radicals, e.g., which are detectable with an electron spin resonance spectrometer; 2) quenching the radicals to an extent that the radicals are at a second level lower than the first level, such as at a level that is no longer detectable with the electron spin resonance spectrometer, e.g., such as at a level of less than about 10¹⁴ spins; and 3) processing the irradiated biomass feedstock to produce a product. If desired, prior to irradiation and/or after irradiation, the biomass feedstock can be prepared by reducing one or more dimensions of individual pieces of the biomass feedstock.

In some implementations, the processing step includes making a product, such as a fuel, such as a combustible fuel, such as a motor, an aviation fuel or a fuel cell fuel, e.g., for generating electricity, by converting the irradiated biomass feedstock with a microorganism having the ability to convert at least a portion, e.g., at least about 1 percent by weight, of the biomass to the product.

In some embodiments, irradiating is performed on the biomass feedstock while the biomass feedstock is exposed to air, nitrogen, oxygen, helium, or argon. In some embodiments, pretreatment can include pretreating the biomass feedstock with steam explosion.

In some embodiments, the method further includes reducing one or more dimensions of individual pieces of biomass, for example by shearing, wet or dry grinding, cutting, squeezing, compressing or mixtures of any of these processes. For example, shearing can be performed with a rotary knife cutter. The shearing can produce fibers having an average length-to-diameter ratio of greater than 5/1. In some embodiments, the prepared biomass can have a BET surface area of greater than 0.25 m²/g. The biomass can be sheared to an extent that internal fibers of the biomass are substantially exposed. The biomass can be sheared to an extent that it has a bulk density of less than about 0.35 g/cm³.

In some embodiments, the process does not include hydrolyzing the biomass with an acid or a base. For example, at least about seventy percent by weight of the biomass can be un-hydrolyzed, e.g., at least at 95 percent by weight of the biomass has not been hydrolyzed. In specific embodiments, substantially none of the biomass has been hydrolyzed.

In some embodiments, irradiation is performed on biomass in which less than about 25 percent by weight of the biomass is wetted with a liquid, such as water. Specifically, in some embodiments, at least one pretreatment method is performed on biomass in which substantially none of the biomass is wetted with a liquid, such as water. The biomass can have, e.g., less than about five percent by weight retained water, measured at 25° C. and at fifty percent relative humidity.

In some embodiments, irradiation is performed on biomass in which less than about 25 percent by weight of the biomass is in a swollen state, the swollen state being characterized as having a volume of more than about 2.5 percent higher than an unswollen state. In other embodiments, the biomass is mixed with or includes a swelling agent.

Pressure can be utilized in any of the methods described herein. For example, irradiation can be performed on the biomass under a pressure of greater than about 2.5 atmospheres, such as greater than 5 or 10 atmospheres.

Examples of biomass feedstock include paper, paper products, paper waste, wood, particle board, sawdust, agricultural waste, sewage, silage, grasses, rice hulls, bagasse, cotton, jute, hemp, flax, bamboo, sisal, abaca, straw, corn cobs, corn stover, switchgrass, alfalfa, hay, rice hulls, coconut hair, cotton, synthetic celluloses, seaweed, algae, or mixtures of these. The biomass can be or can include a natural or a synthetic material.

Examples of fuels include one or more of hydrogen, alcohols, and hydrocarbons. For example, the alcohols can be ethanol, n-propanol, isopropanol, n-butanol, or mixtures of these.

Irradiation can be, e.g., performed utilizing an ionizing radiation, such as gamma rays, a beam of electrons, or ultraviolet C radiation having a wavelength of from about 100 nm to about 280 nm. Irradiation can be performed using multiple applications of radiation. The ionizing radiation can include electron beam radiation. For example, the radiation can be applied at a total dose of between about 10 Mrad and about 150 Mrad, such as at a dose rate of about 0.5 to about 10 Mrad/day, or 1 Mrad/s to about 10 Mrad/s. In some embodiments, irradiating includes applying two or more radiation sources, such as gamma rays and a beam of electrons.

In some embodiments, the biomass includes a first cellulose having a first number average molecular weight and the carbohydrate material comprises a second cellulose having a second number average molecular weight lower than the first number average molecular weight. For example, the second number average molecular weight is lower than the first number average molecular weight by more than about one-fold. In some embodiments, the first cellulose has a first crystallinity, and the second cellulose has a second crystallinity lower than the first crystallinity. For example, the second crystallinity can be lower than the first crystallinity by more than about 10 percent.

In some embodiments, the first cellulose can have a first level of oxidation and the second cellulose has a second level of oxidation higher than the first level of oxidation.

The biomass material can further include a buffer, such as sodium bicarbonate or ammonium chloride, an electrolyte, such as potassium chloride or sodium chloride a growth factor, such as biotin and/or a base pair such as uracil, a surfactant, a mineral, or a chelating agent.

In some embodiments, the methods include pretreating with one or more other pretreatment methods in addition to irradiation. For example, the two or more different pretreatment methods can include radiation and sonication, radiation and oxidation, and radiation and pyrolization. Optionally, pretreating the biomass can include steam explosion.

To further aid in the reduction of the molecular weight of the biomass, an enzyme, e.g., a cellulolytic enzyme, or a chemical, e.g., sodium hypochlorite, an acid, a base or a swelling agent, can be utilized with any method described herein. The enzyme and/or chemical treatment can occur before, during or after irradiation or other pretreatment.

When a microorganism is utilized, it can be a natural microorganism or an engineered microorganism. For example, the microorganism can be a bacterium, e.g., a cellulolytic bacterium, a fungus, e.g., a yeast, a plant or a protist, e.g., an algae, a protozoa or a fungus-like protist, e.g., a slime mold. When the organisms are compatible, mixtures may be utilized. Generally, various microorganisms can produce a number of useful products, such as a fuel, by operating on, e.g., fermenting the materials. For example, alcohols, organic acids, hydrocarbons, hydrogen, proteins or mixtures of any of these materials can be produced by fermentation or other processes.

Examples of products that may be produced using the methods disclosed herein include mono- and polyfunctional C1-C6 alkyl alcohols, mono- and poly-functional carboxylic acids, C1-C6 hydrocarbons, and combinations thereof. Specific examples of suitable alcohols include methanol, ethanol, propanol, isopropanol, butanol, ethylene glycol, propylene glycol, 1,4-butane diol, glycerin, and combinations thereof. Specific example of suitable carboxylic acids include formic acid, acetic acid, propionic acid, butyric acid, valeric acid, caproic acid, palmitic acid, stearic acid, oxalic acid, malonic acid, succinic acid, glutaric acid, oleic acid, linoleic acid, glycolic acid, lactic acid, γ-hydroxybutyric acid, and combinations thereof. Examples of suitable hydrocarbons include methane, ethane, propane, pentane, n-hexane, and combinations thereof. Many of these products may be used as fuels. Other products are described in U.S. Provisional Application Ser. No. 61/139,453, the full disclosure of which is incorporated by reference herein. Products or co-products produced can be products intended to be used as produced or the products produced can be intermediates for any other process described herein or any process described in any application incorporated by reference herein.

Examples of microorganisms that may be used to produce useful products include bacteria, yeasts, or combinations thereof. For example, the microorganism can be a bacterium, e.g., a cellulolytic bacterium, a fungus, e.g., a yeast, a plant or a protist, e.g., an algae, a protozoa or a fungus-like protist, e.g., a slime mold.

In any of the methods disclosed herein, radiation may be applied from a device that is in a vault.

The term “fibrous material,” as used herein, is a material that includes numerous loose, discrete and separable fibers. For example, a fibrous material can be prepared from a bleached Kraft paper fiber source by shearing, e.g., with a rotary knife cutter.

The term “screen,” as used herein, means a member capable of sieving material according to size. Examples of screens include a perforated plate, cylinder or the like, or a wire mesh or cloth fabric.

The term “pyrolysis,” as used herein, means to break bonds in a material by the application of heat energy. Pyrolysis can occur while the subject material is under vacuum, or immersed in a gaseous material, such as an oxidizing gas, e.g., air or oxygen, or a reducing gas, such as hydrogen.

Oxygen content is measured by elemental analysis by pyrolyzing a sample in a furnace operating at 1300° C. or above.

The term “biomass” includes any non-fossilized, i.e., renewable, organic matter. The various types of biomass include plant biomass (defined below), microbial biomass, animal biomass (any animal by-product, animal waste, etc.) and municipal waste biomass (residential and light commercial refuse with recyclables such as metal and glass removed). The term biomass also includes virgin or post consumer cellulosic materials, such as rags and towels fabricated from cotton or a cotton blend.

The term “plant biomass” and “lignocellulosic biomass” refer to virtually any plant-derived organic matter (woody or non-woody). Plant biomass can include, but is not limited to, agricultural or food crops (e.g., sugarcane, sugar beets or corn kernels) or an extract therefrom (e.g., sugar from sugarcane and corn starch from corn), agricultural crops and agricultural crop wastes and residues such as corn stover, wheat straw, rice straw, sugar cane bagasse, cotton and the like. Plant biomass further includes, but is not limited to, trees, woody energy crops, wood wastes and residues such as softwood forest thinnings, barky wastes, sawdust, paper and pulp industry waste streams, wood fiber, and the like. Additionally, grass crops, such as switchgrass and the like have potential to be produced on a large-scale as another plant biomass source. For urban areas, the best potential plant biomass feedstock includes yard waste (e.g., grass clippings, leaves, tree clippings, and brush) and vegetable processing waste.

“Lignocellulosic feedstock,” is any type of plant biomass such as, but not limited to, non-woody plant biomass, cultivated crops, such as, but not limited to, grasses, for example, but not limited to, C4 grasses, such as switchgrass, cord grass, rye grass, miscanthus, reed canary grass, or a combination thereof, or sugar processing residues such as bagasse, or beet pulp, agricultural residues, for example, soybean stover, corn stover, rice straw, rice hulls, barley straw, corn cobs, wheat straw, canola straw, rice straw, oat straw, oat hulls, corn fiber, recycled wood pulp fiber, sawdust, hardwood, for example aspen wood and sawdust, softwood, or a combination thereof. Further, the lignocellulosic feedstock may include cellulosic waste material such as, but not limited to, newsprint, cardboard, sawdust, and the like.

Lignocellulosic feedstock may include one species of fiber or alternatively, lignocellulosic feedstock may include a mixture of fibers that originate from different lignocellulosic feedstocks. Furthermore, the lignocellulosic feedstock may comprise fresh lignocellulosic feedstock, partially dried lignocellulosic feedstock, fully dried lignocellulosic feedstock or a combination thereof.

For the purposes of this disclosure, carbohydrates are materials that are composed entirely of one or more saccharide units or that include one or more saccharide units. The saccharide units can be functionalized about the ring with one or more functional groups, such as carboxylic acid groups, amino groups, nitro groups, nitroso groups or nitrile groups and still be considered carbohydrates. Carbohydrates can be polymeric (e.g., equal to or greater than 10-mer, 100-mer, 1,000-mer, 10,000-mer, or 100,000-mer), oligomeric (e.g., equal to or greater than a 4-mer, 5-mer, 6-mer, 7-mer, 8-mer, 9-mer or -mer), trimeric, dimeric, or monomeric. When the carbohydrates are formed of more than a single repeat unit, each repeat unit can be the same or different.

Examples of polymeric carbohydrates include cellulose, xylan, pectin, and starch, while cellobiose and lactose are examples of dimeric carbohydrates. Examples of monomeric carbohydrates include glucose and xylose.

Carbohydrates can be part of a supramolecular structure, e.g., covalently bonded into the structure. Examples of such materials include lignocellulosic materials, such as those found in wood.

A starchy material is one that is or includes significant amounts of starch or a starch derivative, such as greater than about 5 percent by weight starch or starch derivative. For purposes of this disclosure, a starch is a material that is or includes an amylose, an amylopectin, or a physical and/or chemical mixture thereof, e.g., a 20:80 or 30:70 percent by weight mixture of amylose to amylopectin. For example, rice, corn, and mixtures thereof are starchy materials. Starch derivatives include, e.g., maltodextrin, acid-modified starch, base-modified starch, bleached starch, oxidized starch, acetylated starch, acetylated and oxidized starch, phosphate-modified starch, genetically-modified starch and starch that is resistant to digestion.

For purposes of this disclosure, a low molecular weight sugar is a carbohydrate or a derivative thereof that has a formula weight (excluding moisture) that is less than about 2,000, e.g., less than about 1,800, 1,600, less than about 1,000, less than about 500, less than about 350 or less than about 250. For example, the low molecular weight sugar can be a monosaccharide, e.g., glucose or xylose, a disaccharide, e.g., cellobiose or sucrose, or a trisaccharide.

A combustible fuel is a material capable of burning in the presence of oxygen. Examples of combustible fuels include ethanol, n-propanol, n-butanol, hydrogen and mixtures of any two or more of these.

Swelling agents as used herein are materials that cause a discernable swelling, e.g., a 2.5 percent increase in volume over an unswollen state of cellulosic and/or lignocellulosic materials, when applied to such materials as a solution, e.g., a water solution. Examples include alkaline substances, such as sodium hydroxide, potassium hydroxide, lithium hydroxide and ammonium hydroxides, acidifying agents, such as mineral acids (e.g., sulfuric acid, hydrochloric acid and phosphoric acid), salts, such as zinc chloride, calcium carbonate, sodium carbonate, benzyltrimethylammonium sulfate, and basic organic amines, such as ethylene diamine.

A “sheared material,” as used herein, is a material that includes discrete fibers in which at least about 50% of the discrete fibers have a length/diameter (L/D) ratio of at least about 5, and that has an uncompressed bulk density of less than about 0.6 g/cm³. A sheared material is thus different from a material that has been cut, chopped or ground.

Changing a molecular structure of a biomass feedstock, as used herein, means to change the chemical bonding arrangement, such as the type and quantity of functional groups or conformation of the structure. For example, the change in the molecular structure can include changing the supramolecular structure of the material, oxidation of the material, changing an average molecular weight, changing an average crystallinity, changing a surface area, changing a degree of polymerization, changing a porosity, changing a degree of branching, grafting on other materials, changing a crystalline domain size, or an changing an overall domain size.

This application incorporates by reference herein the entire contents of International Application No. PCT/TJS2007/022719, filed on Oct. 26, 2007. The full disclosures of each of the following U.S. patent applications, which are being filed concurrently herewith, are hereby incorporated by reference herein: Attorney Docket Nos. 08995-0062001, 08895-0063001, 08895-0070001, 08895-0075001, 08895-0076001, 08895-0085001, 08895-0086001, 08895-0096001, and 08895-0103001.

Unless otherwise defined, all technical and scientific terms used herein have the same meaning as commonly understood by one of ordinary skill in the art to which this invention belongs. Although methods and materials similar or equivalent to those described herein can be used in the practice or testing of the present invention, suitable methods and materials are described below. All publications, patent applications, patents, and other references mentioned herein are incorporated by reference in their entirety. In case of conflict, the present specification, including definitions, will control. In addition, the materials, methods, and examples are illustrative only and not intended to be limiting.

Other features and advantages of the invention will be apparent from the following detailed description, and from the claims.

DESCRIPTION OF DRAWINGS

FIG. 1 is a block diagram illustrating conversion of biomass into products and co-products.

FIG. 2 is block diagram illustrating conversion of a fiber source into a first and second fibrous material.

FIG. 3 is a cross-sectional view of a rotary knife cutter.

FIG. 4 is block diagram illustrating conversion of a fiber source into a first, second and third fibrous material.

FIG. 5 is block diagram illustrating densification of a material.

FIG. 6 is a perspective view of a pellet mill.

FIG. 7A is a densified fibrous material in pellet form.

FIG. 7B is a transverse cross-section of a hollow pellet in which a center of the hollow is in-line with a center of the pellet.

FIG. 7C is a transverse cross-section of a hollow pellet in which a center of the hollow is out of line with the center of the pellet.

FIG. 7D is a transverse cross-section of a tri-lobal pellet.

FIG. 8 is a block diagram illustrating a treatment sequence for processing feedstock.

FIG. 9 is a perspective, cut-away view of a gamma irradiator housed in a concrete vault.

FIG. 10 is an enlarged perspective view of region R of FIG. 9.

FIG. 11A is a block diagram illustrating an electron beam irradiation feedstock pretreatment sequence.

FIG. 11B is a schematic representation of biomass being ionized, and then oxidized or quenched.

FIG. 12 is a schematic view of a system for sonicating a process stream of cellulosic material in a liquid medium.

FIG. 13 is a schematic view of a sonicator having two transducers coupled to a single horn.

FIG. 14 is a block diagram illustrating a pyrolytic feedstock pretreatment system.

FIG. 15 is a cross-sectional side view of a pyrolysis chamber.

FIG. 16 is a cross-sectional side view of a pyrolysis chamber.

FIG. 17 is a cross-sectional side view of a pyrolyzer that includes a heated filament.

FIG. 18 is a schematic cross-sectional side view of a Curie-Point pyrolyzer.

FIG. 19 is a schematic cross-sectional side view of a furnace pyrolyzer.

FIG. 20 is a schematic cross-sectional top view of a laser pyrolysis apparatus.

FIG. 21 is a schematic cross-sectional top view of a tungsten filament flash pyrolyzer.

FIG. 22 is a block diagram illustrating an oxidative feedstock pretreatment system.

FIG. 23 is block diagram illustrating a general overview of the process of converting a fiber source into a product, e.g., ethanol.

FIG. 24 is a cross-sectional view of a steam explosion apparatus.

FIG. 25 is a schematic cross-sectional side view of a hybrid electron beam/sonication device.

FIG. 26 is a scanning electron micrograph of a fibrous material produced from polycoated paper at 25× magnification. The fibrous material was produced on a rotary knife cutter utilizing a screen with ⅛ inch openings.

FIG. 27 is a scanning electron micrograph of a fibrous material produced from bleached Kraft board paper at 25× magnification. The fibrous material was produced on a rotary knife cutter utilizing a screen with ⅛ inch openings.

FIG. 28 is a scanning electron micrograph of a fibrous material produced from bleached Kraft board paper at 25× magnification. The fibrous material was twice sheared on a rotary knife cutter utilizing a screen with 1/16 inch openings during each shearing.

FIG. 29 is a scanning electron micrograph of a fibrous material produced from bleached Kraft board paper at 25× magnification. The fibrous material was thrice sheared on a rotary knife cutter. During the first shearing, a ⅛ inch screen was used; during the second shearing, a 1/16 inch screen was used, and during the third shearing a 1/32 inch screen was used.

FIGS. 29A-29F are 3-D Raman spectra from the surface of fibers from samples P132, P132-10, P132-100, P-1e, P-30e, and P-100e, respectively.

FIG. 30 is a schematic side view of a sonication apparatus, while FIG. 31 is a cross-sectional view through the processing cell of FIG. 30.

FIG. 32 is a scanning electron micrograph at 1000× magnification of a fibrous material produced from shearing switchgrass on a rotary knife cutter, and then passing the sheared material through a 1/32 inch screen.

FIGS. 33 and 34 are scanning electron micrographs of the fibrous material of FIG. 32 after irradiation with 10 Mrad and 100 Mrad gamma rays, respectively, at 1000× magnification.

FIG. 35 is a scanning electron micrographs of the fibrous material of FIG. 32 after irradiation with 10 Mrad and sonication at 1000× magnification.

FIG. 36 is a scanning electron micrographs of the fibrous material of FIG. 32 after irradiation with 100 Mrad and sonication at 1000× magnification.

FIG. 37 is an infrared spectrum of Kraft board paper sheared on a rotary knife cutter.

FIG. 38 is an infrared spectrum of the Kraft paper of FIG. 37 after irradiation with 100 Mrad of gamma radiation.

FIGS. 38A-38I are ¹H-NMR spectra of samples P132, P132-10, P132-100, P-1e, P-5e, P-10e, P-30e, P-70e, and P-100e in Example 23. FIG. 38J is a comparison of the exchangeable proton at ˜16 ppm from FIGS. 38A-38I. FIG. 38K is a ¹³C-NMR of sample P-100e. FIGS. 38L-38M are ¹³C-NMR of sample P-100e with a delay time of 10 seconds. FIG. 38N is a ¹H-NMR at a concentration of 10% wt./wt. of sample P-100e.

FIG. 39 shows glucose concentration vs. time for various feedstocks.

FIGS. 40A, 40B, and 40C show cell concentrations, ethanol concentrations, and percent growth and ethanol production, respectively, for Z. mobilis.

FIGS. 41A, 41B, and 41C show cell concentrations, ethanol concentrations, and percent growth and ethanol production, respectively, for P. stipitis.

FIGS. 42A, 42B, and 42C show cell concentrations, ethanol concentrations, and percent growth and ethanol production, respectively, for S. cerevisiae.

FIG. 43 is a schematic view of a process for biomass conversion.

FIG. 44 is schematic view of another process for biomass conversion.

DETAILED DESCRIPTION

Biomass (e.g., plant biomass, such as those that are or that include one or more low molecular weight sugars, animal biomass, and municipal waste biomass) can be processed to produce useful products such as fuels, e.g., fuels for internal combustion engines, jet engines or feedstocks for fuel cells. In addition, functionalized materials having desired types and amounts of functionality, such as carboxylic acid groups, enol groups, aldehyde groups, ketone groups, nitrile groups, nitro groups, or nitroso groups, can be prepared using the methods described herein. Such functionalized materials can be, e.g., more soluble, easier to utilize by various microorganisms or can be more stable over the long term, e.g., less prone to oxidation. Systems and processes are described herein that can use various biomass materials, such as cellulosic materials, lignocellulosic materials, starchy materials or materials that are or that include low molecular weight sugars, as feedstock materials. Such materials are often readily available, but can be difficult to process, e.g., by fermentation, or can give sub-optimal yields at a slow rate. Feedstock materials are first physically prepared for processing, often by size reduction of raw feedstock materials. Physically prepared feedstock can be pretreated or processed using one or more of radiation, sonication, oxidation, pyrolysis, and steam explosion. The various pretreatment systems and methods can be used in combinations of two, three, or even four of these technologies.

In some cases, to provide materials that include a carbohydrate, such as cellulose, that can be converted by a microorganism to a number of desirable products, such as a combustible fuels (e.g., ethanol, butanol or hydrogen), feedstocks that include one or more saccharide units can be treated by any one or more of the processes described herein. Other products and co-products that can be produced include, for example, human food, animal feed, pharmaceuticals, and nutriceuticals. A number of examples are presented that range from bench scale implementations of individual pretreatment methods to large-scale biomass processing plants.

Types of Biomass

Generally, any biomass material that is or includes carbohydrates composed entirely of one or more saccharide units or that include one or more saccharide units can be processed by any of the methods described herein. For example, the biomass material can be cellulosic or lignocellulosic materials, starchy materials, such as kernels of corn, grains of rice or other foods, or materials that are or that include one or more low molecular weight sugars, such as sucrose or cellobiose.

For example, such materials can include paper, paper products, wood, wood-related materials, particle board, grasses, rice hulls, bagasse, cotton, jute, hemp, flax, bamboo, sisal, abaca, straw, corn cobs, rice hulls, coconut hair, algae, seaweed, cotton, synthetic celluloses, or mixtures of any of these. Suitable materials include those listed in the Summary section, above.

Fiber sources include cellulosic fiber sources, including paper and paper products (e.g., polycoated paper and Kraft paper), and lignocellulosic fiber sources, including wood, and wood-related materials, e.g., particleboard. Other suitable fiber sources include natural fiber sources, e.g., grasses, rice hulls, bagasse, cotton, jute, hemp, flax, bamboo, sisal, abaca, straw, corn cobs, rice hulls, coconut hair; fiber sources high in α-cellulose content, e.g., cotton; and synthetic fiber sources, e.g., extruded yarn (oriented yarn or un-oriented yarn). Natural or synthetic fiber sources can be obtained from virgin scrap textile materials, e.g., remnants or they can be post consumer waste, e.g., rags. When paper products are used as fiber sources, they can be virgin materials, e.g., scrap virgin materials, or they can be post-consumer waste. Aside from virgin raw materials, post-consumer, industrial (e.g., offal), and processing waste (e.g., effluent from paper processing) can also be used as fiber sources. Also, the fiber source can be obtained or derived from human (e.g., sewage), animal or plant wastes. Additional fiber sources have been described in U.S. Pat. Nos. 6,448,307, 6,258,876, 6,207,729, 5,973,035 and 5,952,105.

In some embodiments, the carbohydrate is or includes a material having one or more β-1,4-linkages and having a number average molecular weight between about 3,000 and 50,000. Such a carbohydrate is or includes cellulose (I), which is derived from (β-glucose 1) through condensation of β(1→4)-glycosidic bonds. This linkage contrasts itself with that for α(1→4)-glycosidic bonds present in starch and other carbohydrates.

Starchy materials include starch itself, e.g., corn starch, wheat starch, potato starch or rice starch, a derivative of starch, or a material that includes starch, such as an edible food product or a crop. For example, the starchy material can be arracacha, buckwheat, banana, barley, cassaya, kudzu, oca, sago, sorghum, regular household potatoes, sweet potato, taro, yams, or one or more beans, such as favas, lentils or peas. Blends of these and/or other starchy materials are also considered to be starchy materials. In particular embodiments, the starchy material is derived from corn. Various corn starches and derivatives are described in “Corn Starch,” Corn Refiners Association (11^(th) Edition, 2006), which is attached hereto as Appendix A.

Biomass materials that include low molecular weight sugars can, e.g., include at least about 0.5 percent by weight of the low molecular sugar, e.g., at least about 2, 3, 4, 5, 6, 7, 8, 9, 10, 12.5, 25, 35, 50, 60, 70, 80, 90 or even at least about 95 percent by weight of the low molecular weight sugar. In some instances, the biomass is composed substantially of the low molecular weight sugar, e.g., greater than 95 percent by weight, such as 96, 97, 98, 99 or substantially 100 percent by weight of the low molecular weight sugar.

Biomass materials that include low molecular weight sugars can be agricultural products or food products, such as sugarcane and sugar beets, or an extract therefrom, e.g., juice from sugarcane or sugar beets. Biomass materials that include low molecular weight sugars can be substantially pure extracts, such as raw or crystallized table sugar (sucrose). Low molecular weight sugars include sugar derivatives. For example, the low molecular weight sugars can be oligomeric (e.g., equal to or greater than a 4-mer, 5-mer, 6-mer, 7-mer, 8-mer, 9-mer or 10-mer), trimeric, dimeric, or monomeric. When the carbohydrates are formed of more than a single repeat unit, each repeat unit can be the same or different.

Specific examples of low molecular weight sugars include cellobiose, lactose, sucrose, glucose and xylose, along with derivatives thereof. In some instances, sugar derivatives are more rapidly dissolved in solution or utilized by microbes to provide a useful material, such as ethanol or butanol. Several such sugars and sugar derivatives are shown below.

Blends of any biomass materials described herein can be utilized for making any of the products described herein, such as ethanol. For example, blends of cellulosic materials and starchy materials can be utilized for making any product described herein.

Systems for Treating Biomass

FIG. 1 shows a system 100 for converting biomass, particularly biomass with significant cellulosic and lignocellulosic components and/or starchy components, into useful products and co-products. System 100 includes a feed preparation subsystem 110, a pretreatment subsystem 114, a primary process subsystem 118, and a post-processing subsystem 122. Feed preparation subsystem 110 receives biomass in its raw form, physically prepares the biomass for use as feedstock by downstream processes (e.g., reduces the size of and homogenizes the biomass), and stores the biomass both in its raw and feedstock forms. Biomass feedstock with significant cellulosic and/or lignocellulosic components, or starchy components can have a high average molecular weight and crystallinity that can make processing the feedstock into useful products (e.g., fermenting the feedstock to produce ethanol) difficult. For example, others have used acids, bases and enzymes to process cellulosic, lignocellulosic or starchy feedstocks. As described herein, in some embodiments, such treatments are unnecessary, or are necessary only in small or catalytic amounts.

Pretreatment subsystem 114 receives feedstock from the feed preparation subsystem 110 and prepares the feedstock for use in primary production processes by, for example, reducing the average molecular weight and crystallinity of the feedstock. Primary process subsystem 118 receives pretreated feedstock from pretreatment subsystem 114 and produces useful products (e.g., ethanol, other alcohols, pharmaceuticals, and/or food products). In some cases, the output of primary process subsystem 118 is directly useful but, in other cases, requires further processing provided by post-processing subsystem 122. Post-processing subsystem 122 provides further processing to product streams from primary process system 118 which require it (e.g., distillation and denaturation of ethanol) as well as treatment for waste streams from the other subsystems. In some cases, the co-products of subsystems 114, 118, 122 can also be directly or indirectly useful as secondary products and/or in increasing the overall efficiency of system 100. For example, post-processing subsystem 122 can produce treated water to be recycled for use as process water in other subsystems and/or can produce burnable waste which can be used as fuel for boilers producing steam and/or electricity.

The optimum size for biomass conversion plants is affected by factors including economies of scale and the type and availability of biomass used as feedstock. Increasing plant size tends to increase economies of scale associated with plant processes. However, increasing plant size also tends to increase the costs (e.g., transportation costs) per unit of feedstock. Studies analyzing these factors suggest that the appropriate size for biomass conversion plants can range from 2000 to 10,000 dried tons of feedstock per day depending at least in part on the type of feedstock used. The type of feedstock can also impact plant storage requirements with plants designed primarily for processing feedstock whose availability varies seasonally (e.g., corn stover) requiring more on- or of-site feedstock storage than plants designed to process feedstock whose availability is relatively steady (e.g., waste paper).

Physical Preparation

In some cases, methods of processing begin with a physical preparation of the feedstock e.g., size reduction of raw feedstock materials, such as by cutting, grinding, shearing or chopping. In some cases, loose feedstock (e.g., recycled paper, starchy materials, or switchgrass) is prepared by shearing or shredding. Screens and/or magnets can be used to remove oversized or undesirable objects such as, for example, rocks or nails from the feed stream.

Feed preparation systems can be configured to produce feed streams with specific characteristics such as, for example, specific maximum sizes, specific length-to-width, or specific surface areas ratios. As a part of feed preparation, the bulk density of feedstocks can be controlled (e.g., increased or decreased).

Size Reduction

In some embodiments, the material to be processed is in the form of a fibrous material that includes fibers provided by shearing a fiber source. For example, the shearing can be performed with a rotary knife cutter.

For example, and by reference to FIG. 2, a fiber source 210 is sheared, e.g., in a rotary knife cutter, to provide a first fibrous material 212. The first fibrous material 212 is passed through a first screen 214 having an average opening size of 1.59 mm or less ( 1/16 inch, 0.0625 inch) to provide a second fibrous material 216. If desired, fiber source can be cut prior to the shearing, e.g., with a shredder. For example, when a paper is used as the fiber source, the paper can be first cut into strips that are, e.g., ¼- to ½-inch wide, using a shredder, e.g., a counter-rotating screw shredder, such as those manufactured by Munson (Utica, N.Y). As an alternative to shredding, the paper can be reduced in size by cutting to a desired size using a guillotine cutter. For example, the guillotine cutter can be used to cut the paper into sheets that are, e.g., 10 inches wide by 12 inches long.

In some embodiments, the shearing of fiber source and the passing of the resulting first fibrous material through first screen are performed concurrently. The shearing and the passing can also be performed in a batch-type process.

For example, a rotary knife cutter can be used to concurrently shear the fiber source and screen the first fibrous material. Referring to FIG. 3, a rotary knife cutter 220 includes a hopper 222 that can be loaded with a shredded fiber source 224 prepared by shredding fiber source. Shredded fiber source is sheared between stationary blades 230 and rotating blades 232 to provide a first fibrous material 240. First fibrous material 240 passes through screen 242, and the resulting second fibrous material 244 is captured in bin 250. To aid in the collection of the second fibrous material, the bin can have a pressure below nominal atmospheric pressure, e.g., at least 10 percent below nominal atmospheric pressure, e.g., at least 25 percent below nominal atmospheric pressure, at least 50 percent below nominal atmospheric pressure, or at least 75 percent below nominal atmospheric pressure. In some embodiments, a vacuum source 252 is utilized to maintain the bin below nominal atmospheric pressure.

Shearing can be advantageous for “opening up” and “stressing” the fibrous materials, making the cellulose of the materials more susceptible to chain scission and/or reduction of crystallinity. The open materials can also be more susceptible to oxidation when irradiated.

The fiber source can be sheared in a dry state, a hydrated state (e.g., having up to ten percent by weight absorbed water), or in a wet state, e.g., having between about 10 percent and about 75 percent by weight water. The fiber source can even be sheared while partially or fully submerged under a liquid, such as water, ethanol, isopropanol.

The fiber source can also be sheared in under a gas (such as a stream or atmosphere of gas other than air), e.g., oxygen or nitrogen, or steam.

Other methods of making the fibrous materials include, e.g., stone grinding, mechanical ripping or tearing, pin grinding or air attrition milling.

If desired, the fibrous materials can be separated, e.g., continuously or in batches, into fractions according to their length, width, density, material type, or some combination of these attributes.

For example, ferrous materials can be separated from any of the fibrous materials by passing a fibrous material that includes a ferrous material past a magnet, e.g., an electromagnet, and then passing the resulting fibrous material through a series of screens, each screen having different sized apertures.

The fibrous materials can also be separated, e.g., by using a high velocity gas, e.g., air. In such an approach, the fibrous materials are separated by drawing off different fractions, which can be characterized photonically, if desired. Such a separation apparatus is discussed in Lindsey et al, U.S. Pat. No. 6,883,667.

The fibrous materials can irradiated immediately following their preparation, or they can may be dried, e.g., at approximately 105° C. for 4-18 hours, so that the moisture content is, e.g., less than about 0.5% before use.

If desired, lignin can be removed from any of the fibrous materials that include lignin. Also, to aid in the breakdown of the materials that include the cellulose, the material can be treated prior to irradiation with heat, a chemical (e.g., mineral acid, base or a strong oxidizer such as sodium hypochlorite) and/or an enzyme.

In some embodiments, the average opening size of the first screen is less than 0.79 mm ( 1/32 inch, 0.03125 inch), e.g., less than 0.51 mm ( 1/50 inch, 0.02000 inch), less than 0.40 mm ( 1/64 inch, 0.015625 inch), less than 0.23 mm (0.009 inch), less than 0.20 mm ( 1/128 inch, 0.0078125 inch), less than 0.18 mm (0.007 inch), less than 0.13 mm (0.005 inch), or even less than less than 0.10 mm ( 1/256 inch, 0.00390625 inch). The screen is prepared by interweaving monofilaments having an appropriate diameter to give the desired opening size. For example, the monofilaments can be made of a metal, e.g., stainless steel. As the opening sizes get smaller, structural demands on the monofilaments may become greater. For example, for opening sizes less than 0.40 mm, it can be advantageous to make the screens from monofilaments made from a material other than stainless steel, e.g., titanium, titanium alloys, amorphous metals, nickel, tungsten, rhodium, rhenium, ceramics, or glass. In some embodiments, the screen is made from a plate, e.g. a metal plate, having apertures, e.g., cut into the plate using a laser. In some embodiments, the open area of the mesh is less than 52%, e.g., less than 41%, less than 36%, less than 31%, less than 30%.

In some embodiments, the second fibrous is sheared and passed through the first screen, or a different sized screen. In some embodiments, the second fibrous material is passed through a second screen having an average opening size equal to or less than that of first screen.

Referring to FIG. 4, a third fibrous material 220 can be prepared from the second fibrous material 216 by shearing the second fibrous material 216 and passing the resulting material through a second screen 222 having an average opening size less than the first screen 214.

Generally, the fibers of the fibrous materials can have a relatively large average length-to-diameter ratio (e.g., greater than 20-to-1), even if they have been sheared more than once. In addition, the fibers of the fibrous materials described herein may have a relatively narrow length and/or length-to-diameter ratio distribution.

As used herein, average fiber widths (i.e., diameters) are those determined optically by randomly selecting approximately 5,000 fibers. Average fiber lengths are corrected length-weighted lengths. BET (Brunauer, Emmet and Teller) surface areas are multi-point surface areas, and porosities are those determined by mercury porosimetry.

The average length-to-diameter ratio of the second fibrous material 14 can be, e.g., greater than 8/1, e.g., greater than 10/1, greater than 15/1, greater than 20/1, greater than 25/1, or greater than 50/1. An average length of the second fibrous material 14 can be, e.g., between about 0.5 mm and 2.5 mm, e.g., between about 0.75 mm and 1.0 mm, and an average width (i.e., diameter) of the second fibrous material 14 can be, e.g., between about 5 μm and 50 μm, e.g., between about 10 μm and 30 μm.

In some embodiments, a standard deviation of the length of the second fibrous material 14 is less than 60 percent of an average length of the second fibrous material 14, e.g., less than 50 percent of the average length, less than 40 percent of the average length, less than 25 percent of the average length, less than 10 percent of the average length, less than 5 percent of the average length, or even less than 1 percent of the average length.

In some embodiments, a BET surface area of the second fibrous material is greater than 0.1 m²/g, e.g., greater than 0.25 m²/g, greater than 0.5 m²/g, greater than 1.0 m²/g, greater than 1.5 m²/g, greater than 1.75 m²/g, greater than 5.0 m²/g, greater than 10 m²/g, greater than 25 m²/g, greater than 35 m²/g, greater than 50 m²/g, greater than 60 m²/g, greater than 75 m²/g, greater than 100 m²/g, greater than 150 m²/g, greater than 200 m²/g, or even greater than 250 m²/g. A porosity of the second fibrous material 14 can be, e.g., greater than 20 percent, greater than 25 percent, greater than 35 percent, greater than 50 percent, greater than 60 percent, greater than 70 percent, e.g., greater than 80 percent, greater than 85 percent, greater than 90 percent, greater than 92 percent, greater than 94 percent, greater than 95 percent, greater than 97.5 percent, greater than 99 percent, or even greater than 99.5 percent.

In some embodiments, a ratio of the average length-to-diameter ratio of the first fibrous material to the average length-to-diameter ratio of the second fibrous material is, e.g., less than 1.5, e.g., less than 1.4, less than 1.25, less than 1.1, less than 1.075, less than 1.05, less than 1.025, or even substantially equal to 1.

In particular embodiments, the second fibrous material is sheared again and the resulting fibrous material passed through a second screen having an average opening size less than the first screen to provide a third fibrous material. In such instances, a ratio of the average length-to-diameter ratio of the second fibrous material to the average length-to-diameter ratio of the third fibrous material can be, e.g., less than 1.5, e.g., less than 1.4, less than 1.25, or even less than 1.1.

In some embodiments, the third fibrous material is passed through a third screen to produce a fourth fibrous material. The fourth fibrous material can be, e.g., passed through a fourth screen to produce a fifth material. Similar screening processes can be repeated as many times as desired to produce the desired fibrous material having the desired properties.

Densification

Densified materials can be processed by any of the methods described herein, or any material described herein, e.g., any fibrous material described herein, can be processed by any one or more methods described herein, and then densified as described herein.

A material, e.g., a fibrous material, having a low bulk density can be densified to a product having a higher bulk density. For example, a material composition having a bulk density of 0.05 g/cm³ can be densified by sealing the fibrous material in a relatively gas impermeable structure, e.g., a bag made of polyethylene or a bag made of alternating layers of polyethylene and a nylon, and then evacuating the entrapped gas, e.g., air, from the structure. After evacuation of the air from the structure, the fibrous material can have, e.g., a bulk density of greater than 0.3 g/cm³, e.g., 0.5 g/cm³, 0.6 g/cm³, 0.7 g/cm³ or more, e.g., 0.85 g/cm³. After densification, the product can processed by any of the methods described herein, e.g., irradiated, e.g., with gamma radiation. This can be advantageous when it is desirable to transport the material to another location, e.g., a remote manufacturing plant, where the fibrous material composition can be added to a solution, e.g., to produce ethanol. After piercing the substantially gas impermeable structure, the densified fibrous material can revert to nearly its initial bulk density, e.g., greater than 60 percent of its initial bulk density, e.g., 70 percent, 80 percent, 85 percent or more, e.g., 95 percent of its initial bulk density. To reduce static electricity in the fibrous material, an anti-static agent can be added to the material.

In some embodiments, the structure, e.g., bag, is formed of a material that dissolves in a liquid, such as water. For example, the structure can be formed from a polyvinyl alcohol so that it dissolves when in contact with a water-based system. Such embodiments allow densified structures to be added directly to solutions that include a microorganism, without first releasing the contents of the structure, e.g., by cutting.

Referring to FIG. 5, a biomass material can be combined with any desired additives and a binder, and subsequently densified by application of pressure, e.g., by passing the material through a nip defined between counter-rotating pressure rolls or by passing the material through a pellet mill. During the application of pressure, heat can optionally be applied to aid in the densification of the fibrous material. The densified material can then be irradiated.

In some embodiments, the material prior to densification has a bulk density of less than 0.25 g/cm³, e.g., 0.20 g/cm³, 0.15 g/cm³, 0.10 g/cm³, 0.05 g/cm³ or less, e.g., 0.025 g/cm³. Bulk density is determined using ASTM D 1895B. Briefly, the method involves filling a measuring cylinder of known volume with a sample and obtaining a weight of the sample. The bulk density is calculated by dividing the weight of the sample in grams by the known volume of the cylinder in cubic centimeters.

The preferred binders include binders that are soluble in water, swollen by water, or that has a glass transition temperature of less 25° C., as determined by differential scanning calorimetry. By water-soluble binders, we mean binders having a solubility of at least about 0.05 weight percent in water. By water swellable binders, we mean binders that increase in volume by more than 0.5 percent upon exposure to water.

In some embodiments, the binders that are soluble or swollen by water include a functional group that is capable of forming a bond, e.g., a hydrogen bond, with the fibers of the fibrous material, e.g., cellulosic fibrous material. For example, the functional group can be a carboxylic acid group, a carboxylate group, a carbonyl group, e.g., of an aldehyde or a ketone, a sulfonic acid group, a sulfonate group, a phosphoric acid group, a phosphate group, an amide group, an amine group, a hydroxyl group, e.g., of an alcohol, and combinations of these groups, e.g., a carboxylic acid group and a hydroxyl group. Specific monomeric examples include glycerin, glyoxal, ascorbic acid, urea, glycine, pentaerythritol, a monosaccharide or a disaccharide, citric acid, and tartaric acid. Suitable saccharides include glucose, sucrose, lactose, ribose, fructose, mannose, arabinose and erythrose. Polymeric examples include polyglycols, polyethylene oxide, polycarboxylic acids, polyamides, polyamines and polysulfonic acids polysulfonates. Specific polymeric examples include polypropylene glycol (PPG), polyethylene glycol (PEG), polyethylene oxide, e.g., POLYOX®, copolymers of ethylene oxide and propylene oxide, polyacrylic acid (PAA), polyacrylamide, polypeptides, polyethylenimine, polyvinylpyridine, poly(sodium-4-styrenesulfonate) and poly(2-acrylamido-methyl-1-propanesulfonic acid).

In some embodiments, the binder includes a polymer that has a glass transition temperature less 25° C. Examples of such polymers include thermoplastic elastomers (TPEs). Examples of TPEs include polyether block amides, such as those available under the tradename PEBAX®, polyester elastomers, such as those available under the tradename HYTREL®, and styrenic block copolymers, such as those available under the tradename KRATON®. Other suitable polymers having a glass transition temperature less 25° C. include ethylene vinyl acetate copolymer (EVA), polyolefins, e.g., polyethylene, polypropylene, ethylene-propylene copolymers, and copolymers of ethylene and alpha olefins, e.g., 1-octene, such as those available under the tradename ENGAGE®. In some embodiments, e.g., when the material is a fiberized polycoated paper, the material is densified without the addition of a separate low glass transition temperature polymer.

In a particular embodiment, the binder is a lignin, e.g., a natural or synthetically modified lignin.

A suitable amount of binder added to the material, calculated on a dry weight basis, is, e.g., from about 0.01 percent to about 50 percent, e.g., 0.03 percent, 0.05 percent, 0.1 percent, 0.25 percent, 0.5 percent, 1.0 percent, 5 percent, 10 percent or more, e.g., 25 percent, based on a total weight of the densified material. The binder can be added to the material as a neat, pure liquid, as a liquid having the binder dissolved therein, as a dry powder of the binder, or as pellets of the binder.

The densified fibrous material can be made in a pellet mill. Referring to FIG. 6, a pellet mill 300 has a hopper 301 for holding undensified material 310 that includes a carbohydrate-containing material, such as cellulose. The hopper communicates with an auger 312 that is driven by variable speed motor 314 so that undensified material can be transported to a conditioner 320 that stirs the undensified material with paddles 322 that are rotated by conditioner motor 330. Other ingredients, e.g., any of the additives and/or fillers described herein, can be added at inlet 332. If desired, heat may be added while the fibrous material is in conditioner. After conditioned, the material passes from the conditioner through a dump chute 340, and to another auger 342. The dump chute, as controlled by actuator 344, allows for unobstructed passage of the material from conditioner to auger. Auger is rotated by motor 346, and controls the feeding of the fibrous material into die and roller assembly 350. Specifically, the material is introduced into a hollow, cylindrical die 352, which rotates about a horizontal axis and which has radially extending die holes 250. Die 352 is rotated about the axis by motor 360, which includes a horsepower gauge, indicating total power consumed by the motor. Densified material 370, e.g., in the form of pellets, drops from chute 372 and are captured and processed, such as by irradiation.

The material, after densification, can be conveniently in the form of pellets or chips having a variety of shapes. The pellets can then be irradiated. In some embodiments, the pellets or chips are cylindrical in shape, e.g., having a maximum transverse dimension of, e.g., 1 mm or more, e.g., 2 mm, 3 mm, 5 mm, 8 mm, 10 mm, 15 mm or more, e.g., 25 mm. Other convenient shapes include pellets or chips that are plate-like in form, e.g., having a thickness of 1 mm or more, e.g., 2 mm, 3 mm, 5 mm, 8 mm, 10 mm or more, e.g., 25 mm; a width of, e.g., 5 mm or more, e.g., 10 mm, 15 mm, 25 mm, 30 mm or more, e.g., 50 mm; and a length of 5 mm or more, e.g., 10 mm, 15 mm, 25 mm, 30 mm or more, e.g., 50 mm.

Referring now FIG. 7A-7D, pellets can be made so that they have a hollow inside. As shown, the hollow can be generally in-line with the center of the pellet (FIG. 7B), or out of line with the center of the pellet (FIG. 7C). Making the pellet hollow inside can increase the rate of dissolution in a liquid after irradiation.

Referring now to FIG. 7D, the pellet can have, e.g., a transverse shape that is multi-lobal, e.g., tri-lobal as shown, or tetra-lobal, penta-lobal, hexa-lobal or deca-lobal. Making the pellets in such transverse shapes can also increase the rate of dissolution in a solution after irradiation.

Alternatively, the densified material can be in any other desired form, e.g., the densified material can be in the form of a mat, roll or bale.

EXAMPLES

In one example, half-gallon juice cartons made of un-printed white Kraft board having a bulk density of 20 lb/ft³ can be used as a feedstock. Cartons can be folded flat and then fed into a shredder to produce a confetti-like material having a width of between 0.1 inch and 0.5 inch, a length of between 0.25 inch and 1 inch and a thickness equivalent to that of the starting material (about 0.075 inch). The confetti-like material can be fed to a rotary knife cutter, which shears the confetti-like pieces, tearing the pieces apart and releasing fibrous material.

In some cases, multiple shredder-shearer trains can be arranged in series with output. In one embodiment, two shredder-shearer trains can be arranged in series with output from the first shearer fed as input to the second shredder. In another embodiment, three shredder-shearer trains can be arranged in series with output from the first shearer fed as input to the second shredder and output from the second shearer fed as input to the third shredder. Multiple passes through shredder-shearer trains are anticipated to increase decrease particle size and increase overall surface area within the feedstream.

In another example, fibrous material produced from shredding and shearing juice cartons can be treated to increase its bulk density. In some cases, the fibrous material can be sprayed with water or a dilute stock solution of POLYOX™ WSR N10 (polyethylene oxide) prepared in water. The wetted fibrous material can then be processed through a pellet mill operating at room temperature. The pellet mill can increase the bulk density of the feedstream by more than an order of magnitude.

Pretreatment

Physically prepared feedstock can be pretreated for use in primary production processes by, for example, reducing the average molecular weight and crystallinity of the feedstock and/or increasing the surface area and/or porosity of the feedstock. In some embodiments, the cellulosic and/or lignocellulosic material includes a first cellulose having a first number average molecular weight and the resulting carbohydrate includes a second cellulose having a second number average molecular weight lower than the first number average molecular weight. For example, the second number average molecular weight is lower than the first number average molecular weight by more than about twenty-five percent, e.g., 2×, 3×, 5×, 7×, 10x, 25×, even 100× reduction.

In some embodiments, the first cellulose has a first crystallinity and the second cellulose has a second crystallinity lower than the first crystallinity, such as lower than about two, three, five, ten, fifteen or twenty-five percent lower.

In some embodiments, the first cellulose has a first level of oxidation and the second cellulose has a second level of oxidation higher than the first level of oxidation, such as two, three, four, five, ten or even twenty-five percent higher.

Pretreatment processes can include one or more of irradiation, sonication, oxidation, pyrolysis, and steam explosion. The various pretreatment systems and methods can be used in combinations of two, three, or even four of these technologies.

Pretreatment Combinations

In some embodiments, biomass can be processed by applying two or more of any of the processes described herein, such as two, three, four or more of radiation, sonication, oxidation, pyrolysis, and steam explosion either with or without prior, intermediate, or subsequent feedstock preparation as described herein. The processes can be applied to the biomass in any order or concurrently. For example, a carbohydrate can be prepared by applying radiation, sonication, oxidation, pyrolysis, and, optionally, steam explosion to a cellulosic and/or lignocellulosic material (in any order or concurrently). The provided carbohydrate-containing material can then be converted by one or more microorganisms, such as bacteria, yeast, or mixtures of yeast and bacteria, to a number of desirable products, as described herein. Multiple processes can provide materials that can be more readily utilized by a variety of microorganisms because of their lower molecular weight, lower crystallinity, and/or enhanced solubility. Multiple processes can provide synergies and can reduce overall energy input required in comparison to any single process.

For example, in some embodiments, feedstocks are provided that include a carbohydrate that is produced by a process that includes irradiating and sonicating, irradiating and oxidizing, irradiating and pyrolyzing, or irradiating and steam-exploding (in either order or concurrently) a cellulosic and/or a lignocellulosic material. The provided feedstock can then be contacted with a microorganism having the ability to convert at least a portion, e.g., at least about 1 percent by weight, of the feedstock to the product, such as the combustible fuel.

Pretreatment Conditions

In some embodiments, the process does not include hydrolyzing the cellulosic and/or lignocellulosic material, such as with an acid or a base, e.g., a mineral acid, such as hydrochloric or sulfuric acid. If desired, some or none of the feedstock can include a hydrolyzed material. For example, in some embodiments, at least about seventy percent by weight of the feedstock is an unhydrolyzed material, e.g., at least at 95 percent by weight of the feedstock is an unhydrolyzed material. In some embodiments, substantially all of the feedstock is an unhydrolyzed material.

Any feedstock or any reactor or fermentor charged with a feedstock can include a buffer, such as sodium bicarbonate, ammonium chloride or Tris; an electrolyte, such as potassium chloride, sodium chloride, or calcium chloride; a growth factor, such as biotin and/or a base pair such as uracil or an equivalent thereof, a surfactant, such as Tween® or polyethylene glycol; a mineral, such as such as calcium, chromium, copper, iodine, iron, selenium, or zinc; or a chelating agent, such as ethylene diamine, ethylene diamine tetraacetic acid (EDTA) (or its salt form, e.g., sodium or potassium EDTA), or dimercaprol.

When radiation is utilized, it can be applied to any sample that is dry or wet, or even dispersed in a liquid, such as water. For example, irradiation can be performed on cellulosic and/or lignocellulosic material in which less than about 25 percent by weight of the cellulosic and/or lignocellulosic material has surfaces wetted with a liquid, such as water. In some embodiments, irradiating is performed on cellulosic and/or lignocellulosic material in which substantially none of the cellulosic and/or lignocellulosic material is wetted with a liquid, such as water.

In some embodiments, any processing described herein occurs after the cellulosic and/or lignocellulosic material remains dry as acquired or has been dried, e.g., using heat and/or reduced pressure. For example, in some embodiments, the cellulosic and/or lignocellulosic material has less than about five percent by weight retained water, measured at 25° C. and at fifty percent relative humidity.

If desired, a swelling agent, as defined herein, can be utilized in any process described herein. In some embodiments, when a cellulosic and/or lignocellulosic material is processed using radiation, less than about 25 percent by weight of the cellulosic and/or lignocellulosic material is in a swollen state, the swollen state being characterized as having a volume of more than about 2.5 percent higher than an unswollen state, e.g., more than 5.0, 7.5, 10, or 15 percent higher than the unswollen state. In some embodiments, when radiation is utilized on a cellulosic and/or lignocellulosic material, substantially none of the cellulosic and/or lignocellulosic material is in a swollen state. In specific embodiments when radiation is utilized, the cellulosic and/or lignocellulosic material includes a swelling agent, and swollen cellulosic and/or lignocellulosic receives a dose of less than about 10 Mrad.

When radiation is utilized in any process, it can be applied while the cellulosic and/or lignocellulosic is exposed to air, oxygen-enriched air, or even oxygen itself, or blanketed by an inert gas such as nitrogen, argon, or helium. When maximum oxidation is desired, an oxidizing environment is utilized, such as air or oxygen.

When radiation is utilized, it may be applied to biomass, such as cellulosic and/or lignocellulosic material, under a pressure of greater than about 2.5 atmospheres, such as greater than 5, 10, 15, 20 or even greater than about 50 atmospheres.

Radiation Treatment

One or more irradiation processing sequences can be used to process raw feedstock from a wide variety of different sources to extract useful substances from the feedstock, and to provide partially degraded organic material which functions as input to further processing steps and/or sequences. Irradiation can reduce the molecular weight and/or crystallinity of feedstock. In some embodiments, energy deposited in a material that releases an electron from its atomic orbital is used to irradiate the materials. The radiation may be provided by 1) heavy charged particles, such as alpha particles or protons, 2) electrons, produced, for example, in beta decay or electron beam accelerators, or 3) electromagnetic radiation, for example, gamma rays, x rays, or ultraviolet rays. In one approach, radiation produced by radioactive substances can be used to irradiate the feedstock. In some embodiments, any combination in any order or concurrently of (1) through (3) may be utilized. In another approach, electromagnetic radiation (e.g., produced using electron beam emitters) can be used to irradiate the feedstock. The doses applied depend on the desired effect and the particular feedstock. For example, high doses of radiation can break chemical bonds within feedstock components and low doses of radiation can increase chemical bonding (e.g., cross-linking) within feedstock components. In some instances when chain scission is desirable and/or polymer chain functionalization is desirable, particles heavier than electrons, such as protons, helium nuclei, argon ions, silicon ions, neon ions, carbon ions, phosphorus ions, oxygen ions or nitrogen ions can be utilized. When ring-opening chain scission is desired, positively charged particles can be utilized for their Lewis acid properties for enhanced ring-opening chain scission. For example, when oxygen-containing functional groups are desired, irradiation in the presence of oxygen or even irradiation with oxygen ions can be performed. For example, when nitrogen-containing functional groups are desirable, irradiation in the presence of nitrogen or even irradiation with nitrogen ions can be performed.

Referring to FIG. 8, in one method, a first material 2 that is or includes cellulose having a first number average molecular weight (^(T)M_(N1)) is irradiated, e.g., by treatment with ionizing radiation (e.g., in the form of gamma radiation, X-ray radiation, 100 nm to 280 nm ultraviolet (UV) light, a beam of electrons or other charged particles) to provide a second material 3 that includes cellulose having a second number average molecular weight (^(T)M_(N2)) lower than the first number average molecular weight. The second material (or the first and second material) can be combined with a microorganism (e.g., a bacterium or a yeast) that can utilize the second and/or first material to produce a fuel 5 that is or includes hydrogen, an alcohol (e.g., ethanol or butanol, such as n-, sec- or t-butanol), an organic acid, a hydrocarbon or mixtures of any of these.

Since the second material 3 has cellulose having a reduced molecular weight relative to the first material, and in some instances, a reduced crystallinity as well, the second material is generally more dispersible, swellable and/or soluble in a solution containing a microorganism. These properties make the second material 3 more susceptible to chemical, enzymatic and/or biological attack relative to the first material 2, which can greatly improve the production rate and/or production level of a desired product, e.g., ethanol. Radiation can also sterilize the materials.

In some embodiments, the second number average molecular weight (M_(N2)) is lower than the first number average molecular weight (^(T)M_(N1)) by more than about 10 percent, e.g., 15, 20, 25, 30, 35, 40, 50 percent, 60 percent, or even more than about 75 percent.

In some instances, the second material has cellulose that has as crystallinity (^(T)C₂) that is lower than the crystallinity (^(T)C₁) of the cellulose of the first material. For example, (^(T)C₂) can be lower than (^(T)C₁) by more than about 10 percent, e.g., 15, 20, 25, 30, 35, 40, or even more than about 50 percent.

In some embodiments, the starting crystallinity index (prior to irradiation) is from about 40 to about 87.5 percent, e.g., from about 50 to about 75 percent or from about 60 to about 70 percent, and the crystallinity index after irradiation is from about 10 to about 50 percent, e.g., from about 15 to about 45 percent or from about 20 to about 40 percent. However, in some embodiments, e.g., after extensive irradiation, it is possible to have a crystallinity index of lower than 5 percent. In some embodiments, the material after irradiation is substantially amorphous.

In some embodiments, the starting number average molecular weight (prior to irradiation) is from about 200,000 to about 3,200,000, e.g., from about 250,000 to about 1,000,000 or from about 250,000 to about 700,000, and the number average molecular weight after irradiation is from about 50,000 to about 200,000, e.g., from about 60,000 to about 150,000 or from about 70,000 to about 125,000. However, in some embodiments, e.g., after extensive irradiation, it is possible to have a number average molecular weight of less than about 10,000 or even less than about 5,000.

In some embodiments, the second material can have a level of oxidation (^(T)O₂) that is higher than the level of oxidation (^(T)O₁) of the first material. A higher level of oxidation of the material can aid in its dispersibility, swellability and/or solubility, further enhancing the materials susceptibility to chemical, enzymatic or biological attack. In some embodiments, to increase the level of the oxidation of the second material relative to the first material, the irradiation is performed under an oxidizing environment, e.g., under a blanket of air or oxygen, producing a second material that is more oxidized than the first material. For example, the second material can have more hydroxyl groups, aldehyde groups, ketone groups, ester groups or carboxylic acid groups, which can increase its hydrophilicity.

Ionizing Radiation

Each form of radiation ionizes the biomass via particular interactions, as determined by the energy of the radiation. Heavy charged particles primarily ionize matter via Coulomb scattering; furthermore, these interactions produce energetic electrons that may further ionize matter. Alpha particles are identical to the nucleus of a helium atom and are produced by the alpha decay of various radioactive nuclei, such as isotopes of bismuth, polonium, astatine, radon, francium, radium, several actinides, such as actinium, thorium, uranium, neptunium, curium, californium, americium, and plutonium.

When particles are utilized, they can be neutral (uncharged), positively charged or negatively charged. When charged, the charged particles can bear a single positive or negative charge, or multiple charges, e.g., one, two, three or even four or more charges. In instances in which chain scission is desired, positively charged particles may be desirable, in part, due to their acidic nature. When particles are utilized, the particles can have the mass of a resting electron, or greater, e.g., 500, 1000, 1500, or 2000 or more times the mass of a resting electron. For example, the particles can have a mass of from about 1 atomic unit to about 150 atomic units, e.g., from about 1 atomic unit to about 50 atomic units, or from about 1 to about 25, e.g., 1, 2, 3, 4, 5, 10, 12 or 15 amu. Accelerators used to accelerate the particles can be electrostatic DC, electrodynamic DC, RF linear, magnetic induction linear or continuous wave. For example, cyclotron type accelerators are available from IBA, Belgium, such as the Rhodotron® system, while DC type accelerators are available from RDI, now IBA Industrial, such as the Dynamitron®) Ions and ion accelerators are discussed in Introductory Nuclear Physics, Kenneth S. Krane, John Wiley & Sons, Inc. (1988), Krsto Prelec, FIZIKA B 6 (1997) 4, 177-206, a copy of which is attached as Appendix B, Chu, William T., “Overview of Light-Ion Beam Therapy”, Columbus-Ohio, ICRU-IAEA Meeting, 18-20 Mar. 2006, a copy of which is attached hereto at Appendix C, Twata, Y. et al., “Alternating-Phase-Focused 1H-DTL for Heavy-Ion Medical Accelerators”, Proceedings of EPAC 2006, Edinburgh, Scotland, a copy of which is attached hereto as Appendix D and Leitner, C. M. et al., “Status of the Superconducting ECR Ion Source Venus”, Proceedings of EPAC 2000, Vienna, Austria, which is attached hereto as Appendix E.

Electrons interact via Coulomb scattering and bremsstrahlung radiation produced by changes in the velocity of electrons. Electrons may be produced by radioactive nuclei that undergo beta decay, such as isotopes of iodine, cesium, technetium, and iridium. Alternatively, an electron gun can be used as an electron source via thermionic emission.

Electromagnetic radiation interacts via three processes: photoelectric absorption, Compton scattering, and pair production. The dominating interaction is determined by the energy of the incident radiation and the atomic number of the material. The summation of interactions contributing to the absorbed radiation in cellulosic material can be expressed by the mass absorption coefficient.

Electromagnetic radiation is subclassified as gamma rays, x rays, ultraviolet rays, infrared rays, microwaves, or radio waves, depending on its wavelength.

For example, gamma radiation can be employed to irradiate the materials. Referring to FIGS. 9 and 10 (an enlarged view of region R), a gamma irradiator 10 includes gamma radiation sources 408, e.g., ⁶⁰Co pellets, a working table 14 for holding the materials to be irradiated and storage 16, e.g., made of a plurality iron plates, all of which are housed in a concrete containment chamber (vault) 20 that includes a maze entranceway 22 beyond a lead-lined door 26. Storage 16 includes a plurality of channels 30, e.g., sixteen or more channels, allowing the gamma radiation sources to pass through storage on their way proximate the working table.

In operation, the sample to be irradiated is placed on a working table. The irradiator is configured to deliver the desired dose rate and monitoring equipment is connected to an experimental block 31. The operator then leaves the containment chamber, passing through the maze entranceway and through the lead-lined door. The operator mans a control panel 32, instructing a computer 33 to lift the radiation sources 12 into working position using cylinder 36 attached to a hydraulic pump 40.

Gamma radiation has the advantage of a significant penetration depth into a variety of material in the sample. Sources of gamma rays include radioactive nuclei, such as isotopes of cobalt, calcium, technicium, chromium, gallium, indium, iodine, iron, krypton, samarium, selenium, sodium, thalium, and xenon.

Sources of x rays include electron beam collision with metal targets, such as tungsten or molybdenum or alloys, or compact light sources, such as those produced commercially by Lyncean.

Sources for ultraviolet radiation include deuterium or cadmium lamps. Sources for infrared radiation include sapphire, zinc, or selenide window ceramic lamps.

Sources for microwaves include klystrons, Slevin type RF sources, or atom beam sources that employ hydrogen, oxygen, or nitrogen gases.

Various other irradiating devices may be used in the methods disclosed herein, including field ionization sources, electrostatic ion separators, field ionization generators, thermionic emission sources, microwave discharge ion sources, recirculating or static accelerators, dynamic linear accelerators, van de Graaff accelerators, and folded tandem accelerators. Such devices are disclosed, for example, in U.S. Provisional Application Ser. No. 61/073,665, the complete disclosure of which is incorporated herein by reference.

Electron Beam

In some embodiments, a beam of electrons is used as the radiation source. A beam of electrons has the advantages of high dose rates (e.g., 1, 5, or even 10 Mrad per second), high throughput, less containment, and less confinement equipment. Electrons can also be more efficient at causing chain scission. In addition, electrons having energies of 4-10 MeV can have a penetration depth of 5 to 30 mm or more, such as 40 mm.

Electron beams can be generated, e.g., by electrostatic generators, cascade generators, transformer generators, low energy accelerators with a scanning system, low energy accelerators with a linear cathode, linear accelerators, and pulsed accelerators. Electrons as an ionizing radiation source can be useful, e.g., for relatively thin piles of materials, e.g., less than 0.5 inch, e.g., less than 0.4 inch, 0.3 inch, 0.2 inch, or less than 0.1 inch. In some embodiments, the energy of each electron of the electron beam is from about 0.3 MeV to about 2.0 MeV (million electron volts), e.g., from about 0.5 MeV to about 1.5 MeV, or from about 0.7 MeV to about 1.25 MeV.

FIG. 11A shows a process flow diagram 3000 that includes various steps in an electron beam irradiation feedstock pretreatment sequence. In first step 3010, a supply of dry feedstock is received from a feed source. As discussed above, the dry feedstock from the feed source may be pre-processed prior to delivery to the electron beam irradiation devices. For example, if the feedstock is derived from plant sources, certain portions of the plant material may be removed prior to collection of the plant material and/or before the plant material is delivered by the feedstock transport device. Alternatively, or in addition, as expressed in optional step 3020, the biomass feedstock can be subjected to mechanical processing (e.g., to reduce the average length of fibers in the feedstock) prior to delivery to the electron beam irradiation devices.

In step 3030, the dry feedstock is transferred to a feedstock transport device (e.g., a conveyor belt) and is distributed over the cross-sectional width of the feedstock transport device approximately uniformly by volume. This can be accomplished, for example, manually or by inducing a localized vibration motion at some point in the feedstock transport device prior to the electron beam irradiation processing.

In some embodiments, a mixing system introduces a chemical agent 3045 into the feedstock in an optional process 3040 that produces a slurry. Combining water with the processed feedstock in mixing step 3040 creates an aqueous feedstock slurry that may be transported through, for example, piping rather than using, for example, a conveyor belt.

The next step 3050 is a loop that encompasses exposing the feedstock (in dry or slurry form) to electron beam radiation via one or more (say, N) electron beam irradiation devices. The feedstock slurry is moved through each of the N “showers” of electron beams at step 3052. The movement may either be at a continuous speed through and between the showers, or there may be a pause through each shower, followed by a sudden movement to the next shower. A small slice of the feedstock slurry is exposed to each shower for some predetermined exposure time at step 3053.

Electron beam irradiation devices may be procured commercially from Ion Beam Applications, Louvain-la-Neuve, Belgium or the Titan Corporation, San Diego, Calif. Typical electron energies can be 1 MeV, 2 MeV, 4.5 MeV, 7.5 MeV, or 10 MeV. Typical electron beam irradiation device power can be 1 kW, 5 kW, 10 kW, 20 kW, 50 kW, 100 kW, 250 kW, or 500 kW. Effectiveness of depolymerization of the feedstock slurry depends on the electron energy used and the dose applied, while exposure time depends on the power and dose. Typical doses may take values of 1 kGy, 5 kGy, 10 kGy, 20 kGy, 50 kGy, 100 kGy, or 200 kGy.

Tradeoffs in considering electron beam irradiation device power specifications include cost to operate, capital costs, depreciation, and device footprint. Tradeoffs in considering exposure dose levels of electron beam irradiation would be energy costs and environment, safety, and health (ESH) concerns. Tradeoffs in considering electron energies include energy costs; here, a lower electron energy may be advantageous in encouraging depolymerization of certain feedstock slurry (see, for example, Bouchard, et al, Cellulose (2006) 13: 601-610). Typically, generators are housed in a vault, e.g., of lead or concrete or lead-lined concrete.

It may be advantageous to provide a double-pass of electron beam irradiation in order to provide a more effective depolymerization process. For example, the feedstock transport device could direct the feedstock (in dry or slurry form) underneath and in a reverse direction to its initial transport direction. Double-pass systems can allow thicker feedstock slurries to be processed and can provide a more uniform depolymerization through the thickness of the feedstock slurry.

The electron beam irradiation device can produce either a fixed beam or a scanning beam. A scanning beam may be advantageous with large scan sweep length and high scan speeds, as this would effectively replace a large, fixed beam width. Further, available sweep widths of 0.5 m, 1 m, 2 m or more are available.

Once a portion of feedstock slurry has been transported through the N electron beam irradiation devices, it may be necessary in some embodiments, as in step 3060, to mechanically separate the liquid and solid components of the feedstock slurry. In these embodiments, a liquid portion of the feedstock slurry is filtered for residual solid particles and recycled back to the slurry preparation step 3040. A solid portion of the feedstock slurry is then advanced on to the next processing step 3070 via the feedstock transport device. In other embodiments, the feedstock is maintained in slurry form for further processing.

Electromagnetic Radiation

In embodiments in which the irradiating is performed with electromagnetic radiation, the electromagnetic radiation can have, e.g., energy per photon (in electron volts) of greater than 10² eV, e.g., greater than 10³, 10⁴, 10⁵, 10⁶, or even greater than 107 eV. In some embodiments, the electromagnetic radiation has energy per photon of between 10⁴ and 10⁷, e.g., between 10⁵ and 10⁶ eV. The electromagnetic radiation can have a frequency of, e.g., greater than 10¹⁶ hz, greater than 10¹⁷ hz, 10¹¹, 10¹⁹, 10²⁰, or even greater than 10²¹ hz. In some embodiments, the electromagnetic radiation has a frequency of between 10¹⁸ and 10²² Hz, e.g., between 10¹⁹ to 10²¹ Hz.

Doses

In some embodiments, the irradiating (with any radiation source or a combination of sources) is performed until the material receives a dose of at least 0.25 Mrad, e.g., at least 1.0 Mrad, at least 2.5 Mrad, at least 5.0 Mrad, or at least 10.0 Mrad. In some embodiments, the irradiating is performed until the material receives a dose of between 1.0 Mrad and 6.0 Mrad, e.g., between 1.5 Mrad and 4.0 Mrad.

In some embodiments, the irradiating is performed at a dose rate of between 5.0 and 1500.0 kilorads/hour, e.g., between 10.0 and 750.0 kilorads/hour or between 50.0 and 350.0 kilorads/hours.

In some embodiments, two or more radiation sources are used, such as two or more ionizing radiations. For example, samples can be treated, in any order, with a beam of electrons, followed by gamma radiation and UV light having wavelengths from about 100 nm to about 280 nm. In some embodiments, samples are treated with three ionizing radiation sources, such as a beam of electrons, gamma radiation, and energetic UV light.

Alternatively, in another example, a fibrous material that includes a cellulosic and/or lignocellulosic material is irradiated and, optionally, treated with acoustic energy, e.g., ultrasound.

In one example of the use of radiation as a pretreatment, half-gallon juice cartons made of un-printed polycoated white Kraft board having a bulk density of 20 lb/ft³ are used as a feedstock. Cartons are folded flat and then fed into a sequence of three shredder-shearer trains arranged in series with output from the first shearer fed as input to the second shredder, and output from the second shearer fed as input to the third shredder. The fibrous material produced by the shredder-shearer train can be sprayed with water and processed through a pellet mill operating at room temperature. The densified pellets can be placed in a glass ampoule, which is evacuated under high vacuum and then back-filled with argon gas. The ampoule is sealed under argon. Alternatively, in another example, the ampoule is sealed under an atmosphere of air. The pellets in the ampoule are irradiated with gamma radiation for about 3 hours at a dose rate of about 1 Mrad per hour to provide an irradiated material in which the cellulose has a lower molecular weight than the starting material.

Additives to Enhance Molecular Weight Breakdown During Irradiation

In some embodiments, prior to irradiation, various materials, e.g., solids or liquids, can be added to the biomass to enhance molecular weight reduction. In those instances in which a liquid is utilized, the liquid can be in contact with outer surfaces of the biomass and/or the liquid can be in interior portions of the biomass, e.g., infused into the biomass.

For example, the material can be a neutral weak base, such as alanine, ammonia, ammonia/water mixture, e.g., 25 percent by weight ammonia in water, water, methyl amine, dimethyl amine, trimethyl amine, pyridine, or a anionic base, such as a salt of acetic acid (e.g., sodium acetate), sodium carbonate, sodium bicarbonate or a salt of an ion of hydrogen sulfide (e.g., sodium hydrosulfide).

Alternatively, the material can be a neutral weak acid, such as formic acid, acetic acid, trichloroacetic acid, water, hydrogen sulfide or a cationic acid, such as an ammonium salt.

Quenching and Controlled Functionalization of Biomass

After treatment with one or more ionizing radiations, such as photonic radiation (e.g., X-rays or gamma-rays), e-beam radiation or particles heavier than electrons that are positively or negatively charged (e.g., protons or carbon ions), any of the carbohydrate-containing materials or mixtures described herein become ionized; that is, they include radicals at levels that are detectable with an electron spin resonance spectrometer. The current practical limit of detection of the radicals is about 10¹⁴ spins at room temperature. After ionization, any biomass material that has been ionized can be to reduce the level of radicals in the ionized biomass, e.g., such that the radicals are no longer detectable with the electron spin resonance spectrometer. For example, the radicals can be quenched by the application of a sufficient pressure to the biomass and/or by utilizing a fluid in contact with the ionized biomass, such as a gas or liquid, that reacts with (quenches) the radicals. The use of a gas or liquid to at least aid in the quenching of the radicals also allows the operator to control functionalization of the ionized biomass with a desired amount and kind of functional groups, such as carboxylic acid groups, enol groups, aldehyde groups, nitro groups, nitrile groups, amino groups, alkyl amino groups, alkyl groups, chloroalkyl groups or chlorofluoroalkyl groups. In some instances, such quenching can improve the stability of some of the ionized biomass materials. For example, quenching can improve the resistance of the biomass to oxidation. Functionalization by quenching can also improve the solubility of any biomass described herein, can improve its thermal stability, which can be important in the manufacture of composites and boards described herein, and can improve material utilization by various microorganisms. For example, the functional groups imparted to the biomass material by quenching can act as receptor sites for attachment by microorganisms, e.g., to enhance cellulose hydrolysis by various microorganisms.

FIG. 11B illustrates changing a molecular and/or a supramolecular structure of a biomass feedstock by pretreating the biomass feedstock with ionizing radiation, such as with electrons or ions of sufficient energy to ionize the biomass feedstock, to provide a first level of radicals. As shown in FIG. 11B, if the ionized biomass remains in the atmosphere, it will be oxidized, such as to an extent that carboxylic acid groups are generated by reacting with the atmospheric oxygen. In some instances with some materials, such oxidation is desired because it can aid in the further breakdown in molecular weight of the carbohydrate-containing biomass, and the oxidation groups, e.g., carboxylic acid groups can be helpful for solubility and microorganism utilization in some instances. However, since the radicals can “live” for some time after irradiation, e.g., longer than 1 day, 5 days, 30 days, 3 months, 6 months or even longer than 1 year, material properties can continue to change over time, which in some instances, can be undesirable. Detecting radicals in irradiated samples by electron spin resonance spectroscopy and radical lifetimes in such samples is discussed in Bartolotta et al., Physics in Medicine and Biology, 46 (2001), 461-471 and in Bartolotta et al., Radiation Protection Dosimetry, Vol. 84, Nos. 1-4, pp. 293-296 (1999), which are attached hereto as Appendix F and Appendix G, respectively. As shown in FIG. 11B, the ionized biomass can be quenched to functionalize and/or to stabilize the ionized biomass. At any point, e.g., when the material is “alive”, “partially alive” or fully quenched, the pretreated biomass can be converted into a product, e.g., a fuel, a food, or a composite.

In some embodiments, the quenching includes an application of pressure to the biomass, such as by mechanically deforming the biomass, e.g., directly mechanically compressing the biomass in one, two, or three dimensions, or applying pressure to a fluid in which the biomass is immersed, e.g., isostatic pressing. In such instances, the deformation of the material itself brings radicals, which are often trapped in crystalline domains, in sufficient proximity so that the radicals can recombine, or react with another group. In some instances, the pressure is applied together with the application of heat, such as a sufficient quantity of heat to elevate the temperature of the biomass to above a melting point or softening point of a component of the biomass, such as lignin, cellulose or hemicellulose. Heat can improve molecular mobility in the polymeric material, which can aid in the quenching of the radicals. When pressure is utilized to quench, the pressure can be greater than about 1000 psi, such as greater than about 1250 psi, 1450 psi, 3625 psi, 5075 psi, 7250 psi, 10000 psi or even greater than 15000 psi.

In some embodiments, quenching includes contacting the biomass with a fluid, such as a liquid or gas, e.g., a gas capable of reacting with the radicals, such as acetylene or a mixture of acetylene in nitrogen, ethylene, chlorinated ethylenes or chlorofluoroethylenes, propylene or mixtures of these gases. In other particular embodiments, quenching includes contacting the biomass with a liquid, e.g., a liquid soluble in, or at least capable of penetrating into the biomass and reacting with the radicals, such as a diene, such as 1,5-cyclooctadiene. In some specific embodiments, the quenching includes contacting the biomass with an antioxidant, such as Vitamin E. If desired, the biomass feedstock can include an antioxidant dispersed therein, and the quenching can come from contacting the antioxidant dispersed in the biomass feedstock with the radicals.

Other methods for quenching are possible. For example, any method for quenching radicals in polymeric materials described in Muratoglu et al., U.S. patent application Publication No. 2008/0067724 and Muratoglu et al., U.S. Pat. No. 7,166,650, which are attached as Appendix H and Appendix I, respectively, can be utilized for quenching any ionized biomass material described herein. Furthermore any quenching agent (described as a “sensitizing agent” in the above-noted Muratoglu disclosures) and/or any antioxidant described in either Muratoglu reference can be utilized to quench any ionized biomass material.

Functionalization can be enhanced by utilizing heavy charged ions, such as any of the heavier ions described herein. For example, if it is desired to enhance oxidation, charged oxygen ions can be utilized for the irradiation. If nitrogen functional groups are desired, nitrogen ions or ions that includes nitrogen can be utilized. Likewise, if sulfur or phosphorus groups are desired, sulfur or phosphorus ions can be used in the irradiation.

In some embodiments, after quenching any of the quenched materials described herein can be further treated with one or more of radiation, such as ionizing or non-ionizing radiation, sonication, pyrolysis, and oxidation for additional molecular and/or supramolecular structure change.

In particular embodiments, functionalized materials described herein are treated with an acid, base, nucleophile or Lewis acid for additional molecular and/or supramolecular structure change, such as additional molecular weight breakdown. Examples of acids include organic acids, such as acetic acid and mineral acids, such as hydrochloric, sulfuric and/or nitric acid. Examples of bases include strong mineral bases, such as a source of hydroxide ion, basic ions, such as fluoride ion, or weaker organic bases, such as amines. Even water and sodium bicarbonate, e.g., when dissolved in water, can effect molecular and/or supramolecular structure change, such as additional molecular weight breakdown.

Particle Beam Exposure in Fluids

In some cases, the cellulosic or lignocellulosic materials can be exposed to a particle beam in the presence of one or more additional fluids (e.g., gases and/or liquids). Exposure of a material to a particle beam in the presence of one or more additional fluids can increase the efficiency of the treatment.

In some embodiments, the material is exposed to a particle beam in the presence of a fluid such as air. Particles accelerated in any one or more of the types of accelerators disclosed herein (or another type of accelerator) are coupled out of the accelerator via an output port (e.g., a thin membrane such as a metal foil), pass through a volume of space occupied by the fluid, and are then incident on the material. In addition to directly treating the material, some of the particles generate additional chemical species by interacting with fluid particles (e.g., ions and/or radicals generated from various constituents of air, such as ozone and oxides of nitrogen). These generated chemical species can also interact with the material, and can act as initiators for a variety of different chemical bond-breaking reactions in the material. For example, any oxidant produced can oxidize the material, which can result in molecular weight reduction.

In certain embodiments, additional fluids can be selectively introduced into the path of a particle beam before the beam is incident on the material. As discussed above, reactions between the particles of the beam and the particles of the introduced fluids can generate additional chemical species, which react with the material and can assist in functionalizing the material, and/or otherwise selectively altering certain properties of the material. The one or more additional fluids can be directed into the path of the beam from a supply tube, for example. The direction and flow rate of the fluid(s) that is/are introduced can be selected according to a desired exposure rate and/or direction to control the efficiency of the overall treatment, including effects that result from both particle-based treatment and effects that are due to the interaction of dynamically generated species from the introduced fluid with the material. In addition to air, exemplary fluids that can be introduced into the ion beam include oxygen, nitrogen, one or more noble gases, one or more halogens, and hydrogen.

Irradiating Low Bulk Density Biomass Materials and Cooling Irradiated Biomass

During treatment of biomass materials with ionizing radiation, especially at high dose rates, such as at rates greater then 0.15 Mrad per second, e.g., 0.25 Mrad/s, 0.35 Mrad/s, 0.5 Mrad/s, 0.75 Mrad/s or even greater than 1 Mrad/sec, biomass materials can retain significant quantities of heat so that the temperature of the biomass materials becomes elevated. While higher temperatures can, in some embodiments, be advantageous, e.g., when a faster reaction rate is desired, it is advantageous to control the heating of the biomass to retain control over the chemical reactions initiated by the ionizing radiation, such as cross-linking, chain scission and/or grafting, e.g., to maintain process control. Low bulk density materials, such as those having a bulk density of less than about 0.4 g/cm³, e.g., less than about 0.35, 0.25 or less about 0.15 g/cm³, especially when combined with materials that have thin cross-sections, such as fibers having small transverse dimensions, are generally easier to cool. In addition, photons and particles can generally penetrate further into and through materials having a relatively low bulk density, which can allow for the processing of larger volumes of materials at higher rates, and can allow for the use of photons and particles that having lower energies, e.g., 0.25 Mev, 0.5 MeV, 0.75 MeV or 1.0 MeV, which can reduce safety shielding requirements. For example, in one method of changing a molecular and/or a supramolecular structure of a biomass feedstock, the biomass is pretreated at a first temperature with ionizing radiation, such as photons, electrons or ions (e.g., singularly or multiply charged cations or anions), for a sufficient time and/or a sufficient dose to elevate the biomass feedstock to a second temperature higher than the first temperature. The pretreated biomass is then cooled to a third temperature below the second temperature. Finally, if desired, the cooled biomass can be treated one or more times with radiation, e.g., with ionizing radiation. If desired, cooling can be applied to the biomass after and/or during each radiation treatment.

The biomass feedstock can be physically prepared as discussed above, e.g., by reducing one or more dimensions of individual pieces of the biomass feedstock so that the feedstock can be more efficiently processed, e.g., more easily cooled and/or more easily penetrated by an ionizing radiation.

In some implementations, the ionizing radiation is applied at a total dose of less than 25 Mrad or less than 10 Mrad, such as less than 5 Mrad or less than 2.5 Mrad, and at a rate of more than 0.25 Mrad per second, such as more than 0.5, 0.75 or greater than 1.0 Mrad/s, prior to cooling the biomass.

The pretreating of the biomass feedstock with ionizing radiation can be performed as the biomass feedstock is being pneumatically conveyed in a fluid, such as a in a gas, e.g., nitrogen or air. To aid in molecular weight breakdown and/or functionalization of the materials, the gas can be saturated with any swelling agent described herein and/or water vapor. For example, acidic water vapor can be utilized. To aid in molecular weight breakdown, the water can be acidified with an organic acid, such as formic, or acetic acid, or a mineral acid, such as sulfuric or hydrochloric acid.

The pretreating of the biomass feedstock with ionizing radiation can be performed as the biomass feedstock falls under the influence of gravity. This procedure can effectively reduce the bulk density of the biomass feedstock as it is being processed and can aid in the cooling of the biomass feedstock. For example, the biomass can be conveyed from a first belt at a first height above the ground and then can be captured by a second belt at a second level above the ground lower than the first level. For example, in some embodiments, the trailing edge of the first belt and the leading edge of the second belt define a gap. Advantageously, the ionizing radiation, such as a beam of electrons, protons, or other ions, can be applied at the gap to prevent damage to the biomass conveyance system.

Cooling of the biomass can include contacting the biomass with a fluid, such as a gas, at a temperature below the first or second temperature, such as gaseous nitrogen at or about 77 K. Even water, such as water at a temperature below nominal room temperature (e.g., 25 degrees Celsius) can be utilized.

Often advantageously, the biomass feedstock has internal fibers, and prior to irradiation with the ionizing radiation, the biomass feedstock has been sheared to an extent that its internal fibers are substantially exposed. This shearing can provide a low bulk density material having small cross-sectional dimensions, which can aid in the breakdown and/or functionalization of the biomass. For example, in some embodiments, the biomass is or includes discrete fibers and/or particles having a maximum dimension of not more than about 0.5 mm, such as not more than about 0.25 mm, not more than about 0.1 mm or not more than about 0.05 mm.

In some embodiments, the biomass feedstock to which the ionizing radiation is applied has a bulk density of less than about 0.35 g/cm³, such as less than about 0.3, 0.25, 0.20, or less than about 0.15 g/cm³ during the application of the ionizing radiation. In such embodiments, the biomass feedstock can be cooled, and then ionizing radiation can be applied to the cooled biomass. In some advantageous embodiments, the biomass feedstock is or includes discrete fibers and/or particles having a maximum dimension of not more than about 0.5 mm, such as not more than about 0.25 mm, not more than about 0.1 mm, not more than about 0.05 mm, or not more than about 0.025 mm.

Sonication

One or more sonication processing sequences can be used to process raw feedstock from a wide variety of different sources to extract useful substances from the feedstock, and to provide partially degraded organic material which functions as input to further processing steps and/or sequences. Sonication can reduce the molecular weight and/or crystallinity of feedstock.

Referring again to FIG. 8, in one method, a first material 2 that includes cellulose having a first number average molecular weight (^(T)M_(N1)) is dispersed in a medium, such as water, and sonicated and/or otherwise cavitated, to provide a second material 3 that includes cellulose having a second number average molecular weight (^(T)M_(N2)) lower than the first number average molecular weight. The second material (or the first and second material in certain embodiments) can be combined with a microorganism (e.g., a bacterium or a yeast) that can utilize the second and/or first material to produce a fuel 5 that is or includes hydrogen, an alcohol, an organic acid, a hydrocarbon or mixtures of any of these.

Since the second material has cellulose having a reduced molecular weight relative to the first material, and in some instances, a reduced crystallinity as well, the second material is generally more dispersible, swellable, and/or soluble in a solution containing the microorganism, e.g., at a concentration of greater than 10⁶ microorganisms/mL. These properties make the second material 3 more susceptible to chemical, enzymatic, and/or microbial attack relative to the first material 2, which can greatly improve the production rate and/or production level of a desired product, e.g., ethanol. Sonication can also sterilize the materials, but should not be used while the microorganisms are supposed to be alive.

In some embodiments, the second number average molecular weight (^(T)M_(N2)) is lower than the first number average molecular weight (^(T)M_(N1)) by more than about 10 percent, e.g., 15, 20, 25, 30, 35, 40, 50 percent, 60 percent, or even more than about 75 percent.

In some instances, the second material has cellulose that has as crystallinity (^(T)C₂) that is lower than the crystallinity (^(T)C₁) of the cellulose of the first material. For example, (^(T)C₂) can be lower than (^(T)C₁) by more than about 10 percent, e.g., 15, 20, 25, 30, 35, 40, or even more than about 50 percent.

In some embodiments, the starting crystallinity index (prior to sonication) is from about 40 to about 87.5 percent, e.g., from about 50 to about 75 percent or from about 60 to about 70 percent, and the crystallinity index after sonication is from about 10 to about 50 percent, e.g., from about 15 to about 45 percent or from about 20 to about 40 percent. However, in certain embodiments, e.g., after extensive sonication, it is possible to have a crystallinity index of lower than 5 percent. In some embodiments, the material after sonication is substantially amorphous.

In some embodiments, the starting number average molecular weight (prior to sonication) is from about 200,000 to about 3,200,000, e.g., from about 250,000 to about 1,000,000 or from about 250,000 to about 700,000, and the number average molecular weight after sonication is from about 50,000 to about 200,000, e.g., from about 60,000 to about 150,000 or from about 70,000 to about 125,000. However, in some embodiments, e.g., after extensive sonication, it is possible to have a number average molecular weight of less than about 10,000 or even less than about 5,000.

In some embodiments, the second material can have a level of oxidation (^(T)O₂) that is higher than the level of oxidation (^(T)O₁) of the first material. A higher level of oxidation of the material can aid in its dispersibility, swellability and/or solubility, further enhancing the materials susceptibility to chemical, enzymatic or microbial attack. In some embodiments, to increase the level of the oxidation of the second material relative to the first material, the sonication is performed in an oxidizing medium, producing a second material that is more oxidized than the first material. For example, the second material can have more hydroxyl groups, aldehyde groups, ketone groups, ester groups or carboxylic acid groups, which can increase its hydrophilicity.

In some embodiments, the sonication medium is an aqueous medium. If desired, the medium can include an oxidant, such as a peroxide (e.g., hydrogen peroxide), a dispersing agent and/or a buffer. Examples of dispersing agents include ionic dispersing agents, e.g., sodium lauryl sulfate, and non-ionic dispersing agents, e.g., poly(ethylene glycol).

In other embodiments, the sonication medium is non-aqueous. For example, the sonication can be performed in a hydrocarbon, e.g., toluene or heptane, an ether, e.g., diethyl ether or tetrahydrofuran, or even in a liquefied gas such as argon, xenon, or nitrogen.

Without wishing to be bound by any particular theory, it is believed that sonication breaks bonds in the cellulose by creating bubbles in the medium containing the cellulose, which grow and then violently collapse. During the collapse of the bubble, which can take place in less than a nanosecond, the implosive force raises the local temperature within the bubble to about 5100 K (even higher in some instance; see, e.g., Suslick et al., Nature 434, 52-55) and generates pressures of from a few hundred atmospheres to over 1000 atmospheres or more. It is these high temperatures and pressures that break the bonds. In addition, without wishing to be bound by any particular theory, it is believed that reduced crystallinity arises, at least in part, from the extremely high cooling rates during collapse of the bubbles, which can be greater than about 10¹¹ K/second. The high cooling rates generally do not allow the cellulose to organize and crystallize, resulting in materials that have reduced crystallinity. Ultrasonic systems and sonochemistry are discussed in, e.g., Olli et al., U.S. Pat. No. 5,766,764; Roberts, U.S. Pat. No. 5,828,156; Mason, Chemistry with Ultrasound, Elsevier, Oxford, (1990); Suslick (editor), Ultrasound: its Chemical, Physical and Biological Effects, VCH, Weinheim, (1988); Price, “Current Trends in Sonochemistry” Royal Society of Chemistry, Cambridge, (1992); Suslick et al., Ann. Rev. Mater. Sci. 29, 295, (1999); Suslick et al., Nature 353, 414 (1991); Hiller et al., Phys. Rev. Lett. 69, 1182 (1992); Barber et al., Nature, 352, 414 (1991); Suslick et al., J. Am. Chem. Soc., 108, 5641 (1986); Tang et al., Chem. Comm., 2119 (2000); Wang et al., Advanced Mater., 12, 1137 (2000); Landau et al., J. of Catalysis, 201, 22 (2001); Perkas et al., Chem. Comm., 988 (2001); Nikitenko et al., Angew. Chem. Inter. Ed. (December 2001); Shafi et al., J. Phys. Chem. B 103, 3358 (1999); Avivi et al., J. Amer. Chem. Soc. 121, 4196 (1999); and Avivi et al., J. Amer. Chem. Soc. 122, 4331 (2000).

Sonication Systems

FIG. 12 shows a general system in which a cellulosic material stream 1210 is mixed with a water stream 1212 in a reservoir 1214 to form a process stream 1216. A first pump 1218 draws process stream 1216 from reservoir 1214 and toward a flow cell 1224. Ultrasonic transducer 1226 transmits ultrasonic energy into process stream 1216 as the process stream flows through flow cell 1224. A second pump 1230 draws process stream 1216 from flow cell 1224 and toward subsequent processing.

Reservoir 1214 includes a first intake 1232 and a second intake 1234 in fluid communication with a volume 1236. A conveyor (not shown) delivers cellulosic material stream 1210 to reservoir 1214 through first intake 1232. Water stream 1212 enters reservoir 1214 through second intake 1234. In some embodiments, water stream 1212 enters volume 1236 along a tangent establishing a swirling flow within volume 1236. In certain embodiments, cellulosic material stream 1210 and water stream 1212 can be introduced into volume 1236 along opposing axes to enhance mixing within the volume.

Valve 1238 controls the flow of water stream 1212 through second intake 1232 to produce a desired ratio of cellulosic material to water (e.g., approximately 10% cellulosic material, weight by volume). For example, 2000 tons/day of cellulosic material can be combined with 1 million to 1.5 million gallons/day, e.g., 1.25 million gallons/day, of water.

Mixing of cellulosic material and water in reservoir 1214 is controlled by the size of volume 1236 and the flow rates of cellulosic material and water into the volume. In some embodiments, volume 1236 is sized to create a minimum mixing residence time for the cellulosic material and water. For example, when 2000 tons/day of cellulosic material and 1.25 million gallons/day of water are flowing through reservoir 1214, volume 1236 can be about 32,000 gallons to produce a minimum mixing residence time of about 15 minutes.

Reservoir 1214 includes a mixer 1240 in fluid communication with volume 1236. Mixer 1240 agitates the contents of volume 1236 to disperse cellulosic material throughout the water in the volume. For example, mixer 1240 can be a rotating vane disposed in reservoir 1214. In some embodiments, mixer 1240 disperses the cellulosic material substantially uniformly throughout the water.

Reservoir 1214 further includes an exit 1242 in fluid communication with volume 1236 and process stream 1216. The mixture of cellulosic material and water in volume 1236 flows out of reservoir 1214 via exit 1242. Exit 1242 is arranged near the bottom of reservoir 1214 to allow gravity to pull the mixture of cellulosic material and water out of reservoir 1214 and into process stream 1216.

First pump 1218 (e.g., any of several recessed impeller vortex pumps made by Essco Pumps & Controls, Los Angeles, Calif.) moves the contents of process stream 1216 toward flow cell 1224. In some embodiments, first pump 1218 agitates the contents of process stream 1216 such that the mixture of cellulosic material and water is substantially uniform at inlet 1220 of flow cell 1224. For example, first pump 1218 agitates process stream 1216 to create a turbulent flow that persists along the process stream between the first pump and inlet 1220 of flow cell 1224.

Flow cell 1224 includes a reactor volume 1244 in fluid communication with inlet 1220 and outlet 1222. In some embodiments, reactor volume 1244 is a stainless steel tube capable of withstanding elevated pressures (e.g., 10 bars). In addition or in the alternative, reactor volume 1244 includes a rectangular cross section.

Flow cell 1224 further includes a heat exchanger 1246 in thermal communication with at least a portion of reactor volume 1244. Cooling fluid 1248 (e.g., water) flows into heat exchanger 1246 and absorbs heat generated when process stream 1216 is sonicated in reactor volume 1244. In some embodiments, the flow rate and/or the temperature of cooling fluid 1248 into heat exchanger 1246 is controlled to maintain an approximately constant temperature in reactor volume 1244. In some embodiments, the temperature of reactor volume 1244 is maintained at 20 to 50° C., e.g., 25, 30, 35, 40, or 45° C. Additionally or alternatively, heat transferred to cooling fluid 1248 from reactor volume 1244 can be used in other parts of the overall process.

An adapter section 1226 creates fluid communication between reactor volume 1244 and a booster 1250 coupled (e.g., mechanically coupled using a flange) to ultrasonic transducer 1226. For example, adapter section 1226 can include a flange and O-ring assembly arranged to create a leak tight connection between reactor volume 1244 and booster 1250. In some embodiments, ultrasonic transducer 1226 is a high-powered ultrasonic transducer made by Hielscher Ultrasonics of Teltow, Germany.

In operation, a generator 1252 delivers electricity to ultrasonic transducer 1252. Ultrasonic transducer 1226 includes a piezoelectric element that converts the electrical energy into sound in the ultrasonic range. In some embodiments, the materials are sonicated using sound having a frequency of from about 16 kHz to about 110 kHz, e.g., from about 18 kHz to about 75 kHz or from about 20 kHz to about 40 kHz. (e.g., sound having a frequency of 20 kHz to 40 kHz). In some examples, sonication is performed at a frequency of between about 15 kHz and about 25 kHz, such as between about 18 kHz and 22 kHz. In specific embodiments, sonicating can be performed utilizing a 1 KW or larger horn, e.g., a 2, 3, 4, 5, or even a 10 KW horn.

The ultrasonic energy is then delivered to the working medium through booster 1248. The ultrasonic energy traveling through booster 1248 in reactor volume 1244 creates a series of compressions and rarefactions in process stream 1216 with an intensity sufficient to create cavitation in process stream 1216. Cavitation disaggregates the cellulosic material dispersed in process stream 1216. Cavitation also produces free radicals in the water of process stream 1216. These free radicals act to further break down the cellulosic material in process stream 1216.

In general, 5 to 4000 MJ/m³, e.g., 10, 25, 50, 100, 250, 500, 750, 1000, 2000, or 3000 MJ/m³, of ultrasonic energy is applied to process stream 16 flowing at a rate of about 0.2 m³/s (about 3200 gallons/min). After exposure to ultrasonic energy in reactor volume 1244, process stream 1216 exits flow cell 1224 through outlet 1222. Second pump 1230 moves process stream 1216 to subsequent processing (e.g., any of several recessed impeller vortex pumps made by Essco Pumps & Controls, Los Angeles, Calif.).

While certain embodiments have been described, other embodiments are possible.

As an example, while process stream 1216 has been described as a single flow path, other arrangements are possible. In some embodiments for example, process stream 1216 includes multiple parallel flow paths (e.g., flowing at a rate of 10 gallon/min). In addition or in the alternative, the multiple parallel flow paths of process stream 1216 flow into separate flow cells and are sonicated in parallel (e.g., using a plurality of 16 kW ultrasonic transducers).

As another example, while a single ultrasonic transducer 1226 has been described as being coupled to flow cell 1224, other arrangements are possible. In some embodiments, a plurality of ultrasonic transducers 1226 are arranged in flow cell 1224 (e.g., ten ultrasonic transducers can be arranged in a flow cell 1224). In some embodiments, the sound waves generated by each of the plurality of ultrasonic transducers 1226 are timed (e.g., synchronized out of phase with one another) to enhance the cavitation acting upon process stream 1216.

As another example, while a single flow cell 1224 has been described, other arrangements are possible. In some embodiments, second pump 1230 moves process stream to a second flow cell where a second booster and ultrasonic transducer further sonicate process stream 1216.

As still another example, while reactor volume 1244 has been described as a closed volume, reactor volume 1244 is open to ambient conditions in certain embodiments. In such embodiments, sonication pretreatment can be performed substantially simultaneously with other pretreatment techniques. For example, ultrasonic energy can be applied to process stream 1216 in reactor volume 1244 while electron beams are simultaneously introduced into process stream 1216.

As another example, while a flow-through process has been described, other arrangements are possible. In some embodiments, sonication can be performed in a batch process. For example, a volume can be filled with a 10% (weight by volume) mixture of cellulosic material in water and exposed to sound with intensity from about 50 W/cm² to about 600 W/cm², e.g., from about 75 W/cm² to about 300 W/cm² or from about 95 W/cm² to about 200 W/cm². Additionally or alternatively, the mixture in the volume can be sonicated from about 1 hour to about 24 hours, e.g., from about 1.5 hours to about 12 hours, or from about 2 hours to about 10 hours. In certain embodiments, the material is sonicated for a pre-determined time, and then allowed to stand for a second pre-determined time before sonicating again.

Referring now to FIG. 13, in some embodiments, two electro-acoustic transducers are mechanically coupled to a single horn. As shown, a pair of piezoelectric transducers 60 and 62 is coupled to a slotted bar horn 64 by respective intermediate coupling horns 70 and 72, the latter also being known as booster horns. The mechanical vibrations provided by the transducers, responsive to high frequency electrical energy applied thereto, are transmitted to the respective coupling horns, which may be constructed to provide a mechanical gain, such as a ratio of 1 to 1.2. The horns are provided with a respective mounting flange 74 and 76 for supporting the transducer and horn assembly in a stationary housing.

The vibrations transmitted from the transducers through the coupling or booster horns are coupled to the input surface 78 of the horn and are transmitted through the horn to the oppositely disposed output surface 80, which, during operation, is in forced engagement with a workpiece (not shown) to which the vibrations are applied.

The high frequency electrical energy provided by the power supply 82 is fed to each of the transducers, electrically connected in parallel, via a balancing transformer 84 and a respective series connected capacitor 86 and 90, one capacitor connected in series with the electrical connection to each of the transducers. The balancing transformer is known also as “balun” standing for “balancing unit.” The balancing transformer includes a magnetic core 92 and a pair of identical windings 94 and 96, also termed the primary winding and secondary winding, respectively.

In some embodiments, the transducers include commercially available piezoelectric transducers, such as Branson Ultrasonics Corporation models 105 or 502, each designed for operation at 20 kHz and a maximum power rating of 3 kW. The energizing voltage for providing maximum motional excursion at the output surface of the transducer is 930 volt rms. The current flow through a transducer may vary between zero and 3.5 ampere depending on the load impedance. At 930 volt rms the output motion is approximately 20 microns. The maximum difference in terminal voltage for the same motional amplitude, therefore, can be 186 volt. Such a voltage difference can give rise to large circulating currents flowing between the transducers. The balancing unit 430 assures a balanced condition by providing equal current flow through the transducers, hence eliminating the possibility of circulating currents. The wire size of the windings must be selected for the full load current noted above and the maximum voltage appearing across a winding input is 93 volt.

As an alternative to using ultrasonic energy, high-frequency, rotor-stator devices can be utilized. This type of device produces high-shear, microcavitation forces which can disintegrate biomass in contact with such forces. Two commercially available high-frequency, rotor-stator dispersion devices are the Supraton™ devices manufactured by Krupp Industrietechnik GmbH and marketed by Dorr-Oliver Deutschland GmbH of Connecticut, and the Dispax™ devices manufactured and marketed by Ika-Works, Inc. of Cincinnati, Ohio. Operation of such a microcavitation device is discussed in Stuart, U.S. Pat. No. 5,370,999.

While ultrasonic transducer 1226 has been described as including one or more piezoelectric active elements to create ultrasonic energy, other arrangements are possible. In some embodiments, ultrasonic transducer 1226 includes active elements made of other types of magnetostrictive materials (e.g., ferrous metals). Design and operation of such a high-powered ultrasonic transducer is discussed in Hansen et al., U.S. Pat. No. 6,624,539. In some embodiments, ultrasonic energy is transferred to process stream 16 through an electro-hydraulic system.

While ultrasonic transducer 1226 has been described as using the electromagnetic response of magnetorestrictive materials to produce ultrasonic energy, other arrangements are possible. In some embodiments, acoustic energy in the form of an intense shock wave can be applied directly to process stream 16 using an underwater spark. In some embodiments, ultrasonic energy is transferred to process stream 16 through a thermo-hydraulic system. For example, acoustic waves of high energy density can be produced by applying power across an enclosed volume of electrolyte, thereby heating the enclosed volume and producing a pressure rise that is subsequently transmitted through a sound propagation medium (e.g., process stream 1216). Design and operation of such a thermo-hydraulic transducer is discussed in Hartmann et al., U.S. Pat. No. 6,383,152.

Pyrolysis

One or more pyrolysis processing sequences can be used to process raw feedstock from a wide variety of different sources to extract useful substances from the feedstock, and to provide partially degraded organic material which functions as input to further processing steps and/or sequences.

Referring again to the general schematic in FIG. 8, a first material 2 that includes cellulose having a first number average molecular weight (^(T)M_(N1)) is pyrolyzed, e.g., by heating the first material in a tube furnace, to provide a second material 3 that includes cellulose having a second number average molecular weight (^(T)M_(N2)) lower than the first number average molecular weight. The second material (or the first and second material in certain embodiments) is/are combined with a microorganism (e.g., a bacterium or a yeast) that can utilize the second and/or first material to produce a fuel 5 that is or includes hydrogen, an alcohol (e.g., ethanol or butanol, such as n-, sec or t-butanol), an organic acid, a hydrocarbon or mixtures of any of these.

Since the second material has cellulose having a reduced molecular weight relative to the first material, and in some instances, a reduced crystallinity as well, the second material is generally more dispersible, swellable and/or soluble in a solution containing the microorganism, e.g., at a concentration of greater than 10⁶ microorganisms/mL. These properties make the second material 3 more susceptible to chemical, enzymatic and/or microbial attack relative to the first material 2, which can greatly improve the production rate and/or production level of a desired product, e.g., ethanol. Pyrolysis can also sterilize the first and second materials.

In some embodiments, the second number average molecular weight (^(T)M_(N2)) is lower than the first number average molecular weight (^(T)M_(N1)) by more than about 10 percent, e.g., 15, 20, 25, 30, 35, 40, 50 percent, 60 percent, or even more than about 75 percent.

In some instances, the second material has cellulose that has as crystallinity (^(T)C₂) that is lower than the crystallinity (^(T)C₁) of the cellulose of the first material. For example, (^(T)C₂) can be lower than (^(T)C₁) by more than about 10 percent, e.g., 15, 20, 25, 30, 35, 40, or even more than about 50 percent.

In some embodiments, the starting crystallinity (prior to pyrolysis) is from about 40 to about 87.5 percent, e.g., from about 50 to about 75 percent or from about 60 to about 70 percent, and the crystallinity index after pyrolysis is from about 10 to about 50 percent, e.g., from about 15 to about 45 percent or from about 20 to about 40 percent. However, in certain embodiments, e.g., after extensive pyrolysis, it is possible to have a crystallinity index of lower than 5 percent. In some embodiments, the material after pyrolysis is substantially amorphous.

In some embodiments, the starting number average molecular weight (prior to pyrolysis) is from about 200,000 to about 3,200,000, e.g., from about 250,000 to about 1,000,000 or from about 250,000 to about 700,000, and the number average molecular weight after pyrolysis is from about 50,000 to about 200,000, e.g., from about 60,000 to about 150,000 or from about 70,000 to about 125,000. However, in some embodiments, e.g., after extensive pyrolysis, it is possible to have a number average molecular weight of less than about 10,000 or even less than about 5,000.

In some embodiments, the second material can have a level of oxidation (^(T)O₂) that is higher than the level of oxidation (^(T)O₁) of the first material. A higher level of oxidation of the material can aid in its dispersibility, swellability and/or solubility, further enhancing the materials susceptibility to chemical, enzymatic or microbial attack. In some embodiments, to increase the level of the oxidation of the second material relative to the first material, the pyrolysis is performed in an oxidizing environment, producing a second material that is more oxidized than the first material. For example, the second material can have more hydroxyl groups, aldehyde groups, ketone groups, ester groups or carboxylic acid groups, which can increase its hydrophilicity.

In some embodiments, the pyrolysis of the materials is continuous. In other embodiments, the material is pyrolyzed for a pre-determined time, and then allowed to cool for a second pre-determined time before pyrolyzing again.

Pyrolysis Systems

FIG. 14 shows a process flow diagram 6000 that includes various steps in a pyrolytic feedstock pretreatment system. In first step 6010, a supply of dry feedstock is received from a feed source.

As described above, the dry feedstock from the feed source may be pre-processed prior to delivery to the pyrolysis chamber. For example, if the feedstock is derived from plant sources, certain portions of the plant material may be removed prior to collection of the plant material and/or before the plant material is delivered by the feedstock transport device. Alternatively, or in addition, the biomass feedstock can be subjected to mechanical processing 6020 (e.g., to reduce the average length of fibers in the feedstock) prior to delivery to the pyrolysis chamber.

Following mechanical processing, the feedstock undergoes a moisture adjustment step 6030. The nature of the moisture adjustment step depends upon the moisture content of the mechanically processed feedstock. Typically, pyrolysis of feedstock occurs most efficiently when the moisture content of the feedstock is between about 10% and about 30% (e.g., between 15% and 25%) by weight of the feedstock. If the moisture content of the feedstock is larger than about 40% by weight, the extra thermal load presented by the water content of the feedstock increases the energy consumption of subsequent pyrolysis steps.

In some embodiments, if the feedstock has a moisture content which is larger than about 30% by weight, drier feedstock material 6220 which has a low moisture content can be blended in, creating a feedstock mixture in step 6030 with an average moisture content that is within the limits discussed above. In certain embodiments, feedstock with a high moisture content can simply be dried by dispersing the feedstock material on a moving conveyor that cycles the feedstock through an in-line heating unit. The heating unit evaporates a portion of the water present in the feedstock.

In some embodiments, if the feedstock from step 6020 has a moisture content which is too low (e.g., lower than about 10% by weight), the mechanically processed feedstock can be combined with wetter feedstock material 6230 with a higher moisture content, such as sewage sludge. Alternatively, or in addition, water 6240 can be added to the dry feedstock from step 6020 to increase its moisture content.

In step 6040, the feedstock—now with its moisture content adjusted to fall within suitable limits—can be preheated in an optional preheating step 6040. Preheating step 6040 can be used to increase the temperature of the feedstock to between 75° C. and 150° C. in preparation for subsequent pyrolysis of the feedstock. Depending upon the nature of the feedstock and the particular design of the pyrolysis chamber, preheating the feedstock can ensure that heat distribution within the feedstock remains more uniform during pyrolysis, and can reduce the thermal load on the pyrolysis chamber.

The feedstock is then transported to a pyrolysis chamber to undergo pyrolysis in step 6050. In some embodiments, transport of the feedstock is assisted by adding one or more pressurized gases 6210 to the feedstock stream. The gases create a pressure gradient in a feedstock transport conduit, propelling the feedstock into the pyrolysis chamber (and even through the pyrolysis chamber). In certain embodiments, transport of the feedstock occurs mechanically; that is, a transport system that includes a conveyor such as an auger transports the feedstock to the pyrolysis chamber.

Other gases 6210 can also be added to the feedstock prior to the pyrolysis chamber. In some embodiments, for example, one or more catalyst gases can be added to the feedstock to assist decomposition of the feedstock during pyrolysis. In certain embodiments, one or more scavenging agents can be added to the feedstock to trap volatile materials released during pyrolysis. For example, various sulfur-based compounds such as sulfides can be liberated during pyrolysis, and an agent such as hydrogen gas can be added to the feedstock to cause desulfurization of the pyrolysis products. Hydrogen combines with sulfides to form hydrogen sulfide gas, which can be removed from the pyrolyzed feedstock.

Pyrolysis of the feedstock within the chamber can include heating the feedstock to relatively high temperatures to cause partial decomposition of the feedstock. Typically, the feedstock is heated to a temperature in a range from 150° C. to 1100° C. The temperature to which the feedstock is heated depends upon a number of factors, including the composition of the feedstock, the feedstock average particle size, the moisture content, and the desired pyrolysis products. For many types of biomass feedstock, for example, pyrolysis temperatures between 300° C. and 550° C. are used.

The residence time of the feedstock within the pyrolysis chamber generally depends upon a number of factors, including the pyrolysis temperature, the composition of the feedstock, the feedstock average particle size, the moisture content, and the desired pyrolysis products. In some embodiments, feedstock materials are pyrolyzed at a temperature just above the decomposition temperature for the material in an inert atmosphere, e.g., from about 2° C. above to about 10° C. above the decomposition temperature or from about 3° C. above to about 7° C. above the decomposition temperature. In such embodiments, the material is generally kept at this temperature for greater than 0.5 hours, e.g., greater than 1.0 hour or greater than about 2.0 hours. In other embodiments, the materials are pyrolyzed at a temperature well above the decomposition temperature for the material in an inert atmosphere, e.g., from about 75° C. above to about 175° C. above the decomposition temperature or from about 85° C. above to about 150° C. above the decomposition temperature. In such embodiments, the material is generally kept at this temperature for less than 0.5 hour, e.g., less 20 minutes, less than 10 minutes, less than 5 minutes or less than 2 minutes. In still other embodiments, the materials are pyrolyzed at an extreme temperature, e.g., from about 200° C. above to about 500° C. above the decomposition temperature of the material in an inert environment or from about 250° C. above to about 400° C. above the decomposition temperature. In such embodiments, the material us generally kept at this temperature for less than 1 minute, e.g., less than 30 seconds, 15 seconds, 10 seconds, 5 seconds, 1 second or less than 500 ms. Such embodiments are typically referred to as flash pyrolysis.

In some embodiments, the feedstock is heated relatively rapidly to the selected pyrolysis temperature within the chamber. For example, the chamber can be designed to heat the feedstock at a rate of between 500° C./s and 11,000° C./s, for example from 500° C./s to 1000° C./s.

A turbulent flow of feedstock material within the pyrolysis chamber is usually advantageous, as it ensures relatively efficient heat transfer to the feedstock material from the heating sub-system. Turbulent flow can be achieved, for example, by blowing the feedstock material through the chamber using one or more injected carrier gases 6210. In general, the carrier gases are relatively inert towards the feedstock material, even at the high temperatures in the pyrolysis chamber. Exemplary carrier gases include, for example, nitrogen, argon, methane, carbon monoxide, and carbon dioxide. Alternatively, or in addition, mechanical transport systems such as augers can transport and circulate the feedstock within the pyrolysis chamber to create a turbulent feedstock flow.

In some embodiments, pyrolysis of the feedstock occurs substantially in the absence of oxygen and other reactive gases. Oxygen can be removed from the pyrolysis chamber by periodic purging of the chamber with high pressure nitrogen (e.g., at nitrogen pressures of 2 bar or more). Following purging of the chamber, a gas mixture present in the pyrolysis chamber (e.g., during pyrolysis of the feedstock) can include less than 4 mole % oxygen (e.g., less than 1 mole % oxygen, and even less than 0.5 mole % oxygen). The absence of oxygen ensures that ignition of the feedstock does not occur at the elevated pyrolysis temperatures.

In certain embodiments, relatively small amounts of oxygen can be introduced into the feedstock and are present during pyrolysis. This technique is referred to as oxidative pyrolysis. Typically, oxidative pyrolysis occurs in multiple heating stages. For example, in a first heating stage, the feedstock is heated in the presence of oxygen to cause partial oxidation of the feedstock. This stage consumes the available oxygen in the pyrolysis chamber. Then, in subsequent heating stages, the feedstock temperature is further elevated. With all of the oxygen in the chamber consumed, however, feedstock combustion does not occur, and combustion-free pyrolytic decomposition of the feedstock (e.g., to generate hydrocarbon products) occurs. In general, the process of heating feedstock in the pyrolysis chamber to initiate decomposition is endothermic. However, in oxidative pyrolysis, formation of carbon dioxide by oxidation of the feedstock is an exothermic process. The heat released from carbon dioxide formation can assist further pyrolysis heating stages, thereby lessening the thermal load presented by the feedstock.

In some embodiments, pyrolysis occurs in an inert environment, such as while feedstock materials are bathed in argon or nitrogen gas. In certain embodiments, pyrolysis can occur in an oxidizing environment, such as in air or argon enriched in air. In some embodiments, pyrolysis can take place in a reducing environment, such as while feedstock materials are bathed in hydrogen gas. To aid pyrolysis, various chemical agents, such as oxidants, reductants, acids or bases can be added to the material prior to or during pyrolysis. For example, sulfuric acid can be added, or a peroxide (e.g., benzoyl peroxide) can be added.

As discussed above, a variety of different processing conditions can be used, depending upon factors such as the feedstock composition and the desired pyrolysis products. For example, for cellulose-containing feedstock material, relatively mild pyrolysis conditions can be employed, including flash pyrolysis temperatures between 375° C. and 450° C., and residence times of less than 1 second. As another example, for organic solid waste material such as sewage sludge, flash pyrolysis temperatures between 500° C. and 650° C. are typically used, with residence times of between 0.5 and 3 seconds. In general, many of the pyrolysis process parameters, including residence time, pyrolysis temperature, feedstock turbulence, moisture content, feedstock composition, pyrolysis product composition, and additive gas composition can be regulated automatically by a system of regulators and an automated control system.

Following pyrolysis step 6050, the pyrolysis products undergo a quenching step 6250 to reduce the temperature of the products prior to further processing. Typically, quenching step 6250 includes spraying the pyrolysis products with streams of cooling water 6260. The cooling water also forms a slurry that includes solid, undissolved product material and various dissolved products. Also present in the product stream is a mixture that includes various gases, including product gases, carrier gases, and other types of process gases.

The product stream is transported via in-line piping to a gas separator that performs a gas separation step 6060, in which product gases and other gases are separated from the slurry formed by quenching the pyrolysis products. The separated gas mixture is optionally directed to a blower 6130, which increases the gas pressure by blowing air into the mixture. The gas mixture can be subjected to a filtration step 6140, in which the gas mixture passes through one or more filters (e.g., activated charcoal filters) to remove particulates and other impurities. In a subsequent step 6150, the filtered gas can be compressed and stored for further use. Alternatively, the filtered gas can be subjected to further processing steps 6160. For example, in some embodiments, the filtered gas can be condensed to separate different gaseous compounds within the gas mixture. The different compounds can include, for example, various hydrocarbon products (e.g., alcohols, alkanes, alkenes, alkynes, ethers) produced during pyrolysis. In certain embodiments, the filtered gas containing a mixture of hydrocarbon components can be combined with steam gas 6170 (e.g., a mixture of water vapor and oxygen) and subjected to a cracking process to reduce molecular weights of the hydrocarbon components.

In some embodiments, the pyrolysis chamber includes heat sources that burn hydrocarbon gases such as methane, propane, and/or butane to heat the feedstock. A portion 6270 of the separated gases can be recirculated into the pyrolysis chamber for combustion, to generate process heat to sustain the pyrolysis process.

In certain embodiments, the pyrolysis chamber can receive process heat that can be used to increase the temperature of feedstock materials. For example, irradiating feedstock with radiation (e.g., gamma radiation, electron beam radiation, or other types of radiation) can heat the feedstock materials to relatively high temperatures. The heated feedstock materials can be cooled by a heat exchange system that removes some of the excess heat from the irradiated feedstock. The heat exchange system can be configured to transport some of the heat energy to the pyrolysis chamber to heat (or pre-heat) feedstock material, thereby reducing energy cost for the pyrolysis process.

The slurry containing liquid and solid pyrolysis products can undergo an optional de-watering step 6070, in which excess water can be removed from the slurry via processes such as mechanical pressing and evaporation. The excess water 6280 can be filtered and then recirculated for further use in quenching the pyrolysis decomposition products in step 6250.

The de-watered slurry then undergoes a mechanical separation step 6080, in which solid product material 6110 is separated from liquid product material 6090 by a series of increasingly fine filters. In step 6100, the liquid product material 6090 can then be condensed (e.g., via evaporation) to remove waste water 6190, and purified by processes such as extraction. Extraction can include the addition of one or more organic solvents 6180, for example, to separate products such as oils from products such as alcohols. Suitable organic solvents include, for example, various hydrocarbons and halo-hydrocarbons. The purified liquid products 6200 can then be subjected to further processing steps. Waste water 6190 can be filtered if necessary, and recirculated for further use in quenching the pyrolysis decomposition products in step 6250.

After separation in step 6080, the solid product material 6110 is optionally subjected to a drying step 6120 that can include evaporation of water. Solid material 6110 can then be stored for later use, or subjected to further processing steps, as appropriate.

The pyrolysis process parameters discussed above are exemplary. In general, values of these parameters can vary widely according to the nature of the feedstock and the desired products. Moreover, a wide variety of different pyrolysis techniques, including using heat sources such as hydrocarbon flames and/or furnaces, infrared lasers, microwave heaters, induction heaters, resistive heaters, and other heating devices and configurations can be used.

A wide variety of different pyrolysis chambers can be used to decompose the feedstock. In some embodiments, for example, pyrolyzing feedstock can include heating the material using a resistive heating member, such as a metal filament or metal ribbon. The heating can occur by direct contact between the resistive heating member and the material.

In certain embodiments, pyrolyzing can include heating the material by induction, such as by using a Curie-Point pyrolyzer. In some embodiments, pyrolyzing can include heating the material by the application of radiation, such as infrared radiation. The radiation can be generated by a laser, such as an infrared laser.

In certain embodiments, pyrolyzing can include heating the material with a convective heat. The convective heat can be generated by a flowing stream of heated gas. The heated gas can be maintained at a temperature of less than about 1200° C., such as less than 1000° C., less than 750° C., less than 600° C., less than 400° C. or even less than 300° C. The heated gas can be maintained at a temperature of greater than about 250° C. The convective heat can be generated by a hot body surrounding the first material, such as in a furnace.

In some embodiments, pyrolyzing can include heating the material with steam at a temperature above about 250° C.

An embodiment of a pyrolysis chamber is shown in FIG. 15. Chamber 6500 includes an insulated chamber wall 6510 with a vent 6600 for exhaust gases, a plurality of burners 6520 that generate heat for the pyrolysis process, a transport duct 6530 for transporting the feedstock through chamber 6500, augers 6590 for moving the feedstock through duct 6530 in a turbulent flow, and a quenching system 6540 that includes an auger 6610 for moving the pyrolysis products, water jets 6550 for spraying the pyrolysis products with cooling water, and a gas separator for separating gaseous products 6580 from a slurry 6570 containing solid and liquid products.

Another embodiment of a pyrolysis chamber is shown in FIG. 16. Chamber 6700 includes an insulated chamber wall 6710, a feedstock supply duct 6720, a sloped inner chamber wall 6730, burners 6740 that generate heat for the pyrolysis process, a vent 6750 for exhaust gases, and a gas separator 6760 for separating gaseous products 6770 from liquid and solid products 6780. Chamber 6700 is configured to rotate in the direction shown by arrow 6790 to ensure adequate mixing and turbulent flow of the feedstock within the chamber.

A further embodiment of a pyrolysis chamber is shown in FIG. 17. Filament pyrolyzer 1712 includes a sample holder 1713 with resistive heating element 1714 in the form of a wire winding through the open space defined by the sample holder 1713. Optionally, the heated element can be spun about axis 1715 (as indicated by arrow 1716) to tumble the material that includes the cellulosic material in sample holder 1713. The space 1718 defined by enclosure 1719 is maintained at a temperature above room temperature, e.g., 200 to 250° C. In a typical usage, a carrier gas, e.g., an inert gas, or an oxidizing or reducing gas, traverses through the sample holder 1713 while the resistive heating element is rotated and heated to a desired temperature, e.g., 325° C. After an appropriate time, e.g., 5 to 10 minutes, the pyrolyzed material is emptied from the sample holder. The system shown in FIG. 17 can be scaled and made continuous. For example, rather than a wire as the heating member, the heating member can be an auger screw. Material can continuously fall into the sample holder, striking a heated screw that pyrolizes the material. At the same time, the screw can push the pyrolyzed material out of the sample holder to allow for the entry of fresh, unpyrolyzed material.

Another embodiment of a pyrolysis chamber is shown in FIG. 18, which features a Curie-Point pyrolyzer 1820 that includes a sample chamber 1821 housing a ferromagnetic foil 1822. Surrounding the sample chamber 1821 is an RF coil 1823. The space 1824 defined by enclosure 1825 is maintained at a temperature above room temperature, e.g., 200 to 250° C. In a typical usage, a carrier gas traverses through the sample chamber 1821 while the foil 1822 is inductively heated by an applied RF field to pyrolize the material at a desired temperature.

Yet another embodiment of a pyrolysis chamber is shown in FIG. 19. Furnace pyrolyzer 130 includes a movable sample holder 131 and a furnace 132. In a typical usage, the sample is lowered (as indicated by arrow 137) into a hot zone 135 of furnace 132, while a carrier gas fills the housing 136 and traverses through the sample holder 131. The sample is heated to the desired temperature for a desired time to provide a pyrolyzed product. The pyrolyzed product is removed from the pyrolyzer by raising the sample holder (as indicated by arrow 134).

In certain embodiments, as shown in FIG. 20, a cellulosic target 140 can be pyrolyzed by treating the target, which is housed in a vacuum chamber 141, with laser light, e.g., light having a wavelength of from about 225 nm to about 1500 nm. For example, the target can be ablated at 266 nm, using the fourth harmonic of an Nd-YAG laser (Spectra Physics, GCR170, San Jose, Calif.). The optical configuration shown allows the nearly monochromatic light 143 generated by the laser 142 to be directed using mirrors 144 and 145 onto the target after passing though a lens 146 in the vacuum chamber 141. Typically, the pressure in the vacuum chamber is maintained at less than about 10⁻⁶ mm Hg. In some embodiments, infrared radiation is used, e.g., 1.06 micron radiation from an Nd-YAG laser. In such embodiments, an infrared sensitive dye can be combined with the cellulosic material to produce a cellulosic target. The infrared dye can enhance the heating of the cellulosic material. Laser ablation is described by Blanchet-Fincher et al. in U.S. Pat. No. 5,942,649.

Referring to FIG. 21, in some embodiments, a cellulosic material can be flash pyrolyzed by coating a tungsten filament 150, such as a 5 to 25 mil tungsten filament, with the desired cellulosic material while the material is housed in a vacuum chamber 151. To affect pyrolysis, current is passed through the filament, which causes a rapid heating of the filament for a desired time. Typically, the heating is continued for seconds before allowing the filament to cool. In some embodiments, the heating is performed a number of times to effect the desired amount of pyrolysis.

In certain embodiments, carbohydrate-containing biomass material can be heated in an absence of oxygen in a fluidized bed reactor. If desired, the carbohydrate containing biomass can have relatively thin cross-sections, and can include any of the fibrous materials described herein, for efficient heat transfer. The material can be heated by thermal transfer from a hot metal or ceramic, such as glass beads or sand in the reactor, and the resulting pyrolysis liquid or oil can be transported to a central refinery for making combustible fuels or other useful products.

Oxidation

One or more oxidative processing sequences can be used to process raw feedstock from a wide variety of different sources to extract useful substances from the feedstock, and to provide partially degraded organic material which functions as input to further processing steps and/or sequences.

Referring again to FIG. 8, a first material 2 that includes cellulose having a first number average molecular weight (^(T)M_(N1)) and having a first oxygen content (^(T)O₁) is oxidized, e.g., by heating the first material in a tube furnace in stream of air or oxygen-enriched air, to provide a second material 3 that includes cellulose having a second number average molecular weight (^(T)MN₂) and having a second oxygen content (^(T)O₂) higher than the first oxygen content (^(T)O₁). The second material (or the first and second material in certain embodiments) can be, e.g., combined with a resin, such as a molten thermoplastic resin or a microorganism, to provide a composite 4 having desirable mechanical properties, or a fuel 5.

Such materials can also be combined with a solid and/or a liquid. For example, the liquid can be in the form of a solution and the solid can be particulate in form. The liquid and/or solid can include a microorganism, e.g., a bacterium, and/or an enzyme. For example, the bacterium and/or enzyme can work on the cellulosic or lignocellulosic material to produce a fuel, such as ethanol, or a coproduct, such as a protein. Fuels and coproducts are described in FIBROUS MATERIALS AND COMPOSITES,” U.S. Ser. No. 11/453,951, filed Jun. 15, 2006. The entire contents of each of the foregoing applications are incorporated herein by reference.

In some embodiments, the second number average molecular weight is not more 97 percent lower than the first number average molecular weight, e.g., not more than 95 percent, 90, 85, 80, 75, 70, 65, 60, 55, 50, 45, 40, 30, 20, 12.5, 10.0, 7.5, 5.0, 4.0, 3.0, 2.5, 2.0 or not more than 1.0 percent lower than the first number average molecular weight. The amount of reduction of molecular weight will depend upon the application.

In some embodiments in which the materials are used to make a fuel or a coproduct, the starting number average molecular weight (prior to oxidation) is from about 200,000 to about 3,200,000, e.g., from about 250,000 to about 1,000,000 or from about 250,000 to about 700,000, and the number average molecular weight after oxidation is from about 50,000 to about 200,000, e.g., from about 60,000 to about 150,000 or from about 70,000 to about 125,000. However, in some embodiments, e.g., after extensive oxidation, it is possible to have a number average molecular weight of less than about 10,000 or even less than about 5,000.

In some embodiments, the second oxygen content is at least about five percent higher than the first oxygen content, e.g., 7.5 percent higher, 10.0 percent higher, 12.5 percent higher, 15.0 percent higher or 17.5 percent higher. In some preferred embodiments, the second oxygen content is at least about 20.0 percent higher than the oxygen content of the first material. Oxygen content is measured by elemental analysis by pyrolyzing a sample in a furnace operating 1300° C. or higher. A suitable elemental analyzer is the LECO CHNS-932 analyzer with a VTF-900 high temperature pyrolysis furnace.

In some embodiments, oxidation of first material 200 does not result in a substantial change in the crystallinity of the cellulose. However, in some instances, e.g., after extreme oxidation, the second material has cellulose that has as crystallinity (^(T)C₂) that is lower than the crystallinity (^(T)C₁) of the cellulose of the first material. For example, (^(T)C₂) can be lower than (^(T)C₁) by more than about 5 percent, e.g., 10, 15, 20, or even 25 percent. This can be desirable to enhance solubility of the materials in a liquid, such as a liquid that includes a bacterium and/or an enzyme.

In some embodiments, the starting crystallinity index (prior to oxidation) is from about 40 to about 87.5 percent, e.g., from about 50 to about 75 percent or from about 60 to about 70 percent, and the crystallinity index after oxidation is from about 30 to about 75.0 percent, e.g., from about 35.0 to about 70.0 percent or from about 37.5 to about 65.0 percent. However, in certain embodiments, e.g., after extensive oxidation, it is possible to have a crystallinity index of lower than 5 percent. In some embodiments, the material after oxidation is substantially amorphous.

Without wishing to be bound by any particular theory, it is believed that oxidation increases the number of hydrogen-bonding groups on the cellulose, such as hydroxyl groups, aldehyde groups, ketone groups carboxylic acid groups or anhydride groups, which can increase its dispersibility and/or its solubility (e.g., in a liquid). To further improve dispersibility in a resin, the resin can include a component that includes hydrogen-bonding groups, such as one or more anhydride groups, carboxylic acid groups, hydroxyl groups, amide groups, amine groups or mixtures of any of these groups. In some preferred embodiments, the component includes a polymer copolymerized with and/or grafted with maleic anhydride. Such materials are available from Dupont under the tradename FUSABOND®.

Generally, oxidation of first material 200 occurs in an oxidizing environment. For example, the oxidation can be effected or aided by pyrolysis in an oxidizing environment, such as in air or argon enriched in air. To aid in the oxidation, various chemical agents, such as oxidants, acids or bases can be added to the material prior to or during oxidation. For example, a peroxide (e.g., benzoyl peroxide) can be added prior to oxidation.

Oxidation Systems

FIG. 22 shows a process flow diagram 5000 that includes various steps in an oxidative feedstock pretreatment system. In first step 5010, a supply of dry feedstock is received from a feed source. The feed source can include, for example, a storage bed or container that is connected to an in-line oxidation reactor via a conveyor belt or another feedstock transport device.

As described above, the dry feedstock from the feed source may be pre-processed prior to delivery to the oxidation reactor. For example, if the feedstock is derived from plant sources, certain portions of the plant material may be removed prior to collection of the plant material and/or before the plant material is delivered by the feedstock transport device. Alternatively, or in addition, the biomass feedstock can be subjected to mechanical processing (e.g., to reduce the average length of fibers in the feedstock) prior to delivery to the oxidation reactor.

Following mechanical processing 5020, feedstock 5030 is transported to a mixing system which introduces water 5150 into the feedstock in a mechanical mixing process. Combining water with the processed feedstock in mixing step 5040 creates an aqueous feedstock slurry 5050, which can then be treated with one or more oxidizing agents.

Typically, one liter of water is added to the mixture for every 0.02 kg to 1.0 kg of dry feedstock. The ratio of feedstock to water in the mixture depends upon the source of the feedstock and the specific oxidizing agents used further downstream in the overall process. For example, in typical industrial processing sequences for lignocellulosic biomass, aqueous feedstock slurry 5050 includes from about 0.5 kg to about 1.0 kg of dry biomass per liter of water.

In some embodiments, one or more fiber-protecting additives 5170 can also be added to the feedstock slurry in feedstock mixing step 5040. Fiber-protecting additives help to reduce degradation of certain types of biomass fibers (e.g., cellulose fibers) during oxidation of the feedstock. Fiber-protecting additives can be used, for example, if a desired product from processing a lignocellulosic feedstock includes cellulose fibers. Exemplary fiber-protecting additives include magnesium compounds such as magnesium hydroxide. Concentrations of fiber-protecting additives in feedstock slurry 5050 can be from 0.1% to 0.4% of the dry weight of the biomass feedstock, for example.

In certain embodiments, aqueous feedstock slurry 5050 can be subjected to an optional extraction 5180 with an organic solvent to remove water-insoluble substances from the slurry. For example, extraction of slurry 5050 with one or more organic solvents yields a purified slurry and an organic waste stream 5210 that includes water-insoluble materials such as fats, oils, and other non-polar, hydrocarbon-based substances. Suitable solvents for performing extraction of slurry 5050 include various alcohols, hydrocarbons, and halo-hydrocarbons, for example.

In some embodiments, aqueous feedstock slurry 5050 can be subjected to an optional thermal treatment 5190 to further prepare the feedstock for oxidation. An example of a thermal treatment includes heating the feedstock slurry in the presence of pressurized steam. In fibrous biomass feedstock, the pressurized steam swells the fibers, exposing a larger fraction of fiber surfaces to the aqueous solvent and to oxidizing agents that are introduced in subsequent processing steps.

In certain embodiments, aqueous feedstock slurry 5050 can be subjected to an optional treatment with basic agents 5200. Treatment with one or more basic agents can help to separate lignin from cellulose in lignocellulosic biomass feedstock, thereby improving subsequent oxidation of the feedstock. Exemplary basic agents include alkali and alkaline earth hydroxides such as sodium hydroxide, potassium hydroxide, and calcium hydroxide. In general, a variety of basic agents can be used, typically in concentrations from about 0.01% to about 0.5% of the dry weight of the feedstock.

Aqueous feedstock slurry 5050 is transported (e.g., by an in-line piping system) to a chamber, which can be an oxidation preprocessing chamber or an oxidation reactor. In oxidation preprocessing step 5060, one or more oxidizing agents 5160 are added to feedstock slurry 5050 to form an oxidizing medium. In some embodiments, for example, oxidizing agents 5160 can include hydrogen peroxide. Hydrogen peroxide can be added to slurry 5050 as an aqueous solution, and in proportions ranging from 3% to between 30% and 35% by weight of slurry 5050. Hydrogen peroxide has a number of advantages as an oxidizing agent. For example, aqueous hydrogen peroxide solution is relatively inexpensive, is relatively chemically stable, and is not particularly hazardous relative to other oxidizing agents (and therefore does not require burdensome handling procedures and expensive safety equipment). Moreover, hydrogen peroxide decomposes to form water during oxidation of feedstock, so that waste stream cleanup is relatively straightforward and inexpensive.

In certain embodiments, oxidizing agents 5160 can include oxygen (e.g., oxygen gas) either alone, or in combination with hydrogen peroxide. Oxygen gas can be bubbled into slurry 5050 in proportions ranging from 0.5% to 10% by weight of slurry 5050. Alternatively, or in addition, oxygen gas can also be introduced into a gaseous phase in equilibrium with slurry 5050 (e.g., a vapor head above slurry 5050). The oxygen gas can be introduced into either an oxidation preprocessing chamber or into an oxidation reactor (or into both), depending upon the configuration of the oxidative processing system. Typically, for example, the partial pressure of oxygen in the vapor above slurry 5050 is larger than the ambient pressure of oxygen, and ranges from 0.5 bar to 35 bar, depending upon the nature of the feedstock.

The oxygen gas can be introduced in pure form, or can be mixed with one or more carrier gases. For example, in some embodiments, high-pressure air provides the oxygen in the vapor. In certain embodiments, oxygen gas can be supplied continuously to the vapor phase to ensure that a concentration of oxygen in the vapor remains within certain predetermined limits during processing of the feedstock. In some embodiments, oxygen gas can be introduced initially in sufficient concentration to oxidize the feedstock, and then the feedstock can be transported to a closed, pressurized vessel (e.g., an oxidation reactor) for processing.

In certain embodiments, oxidizing agents 5160 can include nascent oxygen (e.g., oxygen radicals). Typically, nascent oxygen is produced as needed in an oxidation reactor or in a chamber in fluid communication with an oxidation reactor by one or more decomposition reactions. For example, in some embodiments, nascent oxygen can be produced from a reaction between NO and O₂ in a gas mixture or in solution. In certain embodiments, nascent oxygen can be produced from decomposition of HOCl in solution. Other methods by which nascent oxygen can be produced include via electrochemical generation in electrolyte solution, for example.

In general, nascent oxygen is an efficient oxidizing agent due to the relatively high reactivity of the oxygen radical. However, nascent oxygen can also be a relatively selective oxidizing agent. For example, when lignocellulosic feedstock is treated with nascent oxygen, selective oxidation of lignin occurs in preference to the other components of the feedstock such as cellulose. As a result, oxidation of feedstock with nascent oxygen provides a method for selective removal of the lignin fraction in certain feedstocks. Typically, nascent oxygen concentrations of between about 0.5% and 5% of the dry weight of the feedstock are used to effect efficient oxidation.

Without wishing to be bound by theory, it is believed that nascent oxygen reacts with lignocellulosic feedstock according to at least two different mechanisms. In a first mechanism, nascent oxygen undergoes an addition reaction with the lignin, resulting in partial oxidation of the lignin, which solubilizes the lignin in aqueous solution. As a result, the solubilized lignin can be removed from the rest of the feedstock via washing. In a second mechanism, nascent oxygen disrupts butane cross-links and/or opens aromatic rings that are connected via the butane cross-links. As a result, solubility of the lignin in aqueous solution increases, facilitating separation of the lignin fraction from the remainder of the feedstock via washing.

In some embodiments, oxidizing agents 5160 include ozone (O₃). The use of ozone can introduce several chemical handling considerations in the oxidation processing sequence. If heated too vigorously, an aqueous solution of ozone can decompose violently, with potentially adverse consequences for both human system operators and system equipment. Accordingly, ozone is typically generated in a thermally isolated, thick-walled vessel separate from the vessel that contains the feedstock slurry, and transported thereto at the appropriate process stage.

Without wishing to be bound by theory, it is believed that ozone decomposes into oxygen and oxygen radicals, and that the oxygen radicals (e.g., nascent oxygen) are responsible for the oxidizing properties of ozone in the manner discussed above. Ozone typically preferentially oxidizes the lignin fraction in lignocellulosic materials, leaving the cellulose fraction relatively undisturbed.

Conditions for ozone-based oxidation of biomass feedstock generally depend upon the nature of the biomass. For example, for cellulosic and/or lignocellulosic feedstocks, ozone concentrations of from 0.1 g/m³ to 20 g/m³ of dry feedstock provide for efficient feedstock oxidation. Typically, the water content in slurry 5050 is between 10% by weight and 80% by weight (e.g., between 40% by weight and 60% by weight). During ozone-based oxidation, the temperature of slurry 5050 can be maintained between 0° C. and 100° C. to avoid violent decomposition of the ozone.

In some embodiments, feedstock slurry 5050 can be treated with an aqueous, alkaline solution that includes one or more alkali and alkaline earth hydroxides such as sodium hydroxide, potassium hydroxide, and calcium hydroxide, and then treated thereafter with an ozone-containing gas in an oxidation reactor. This process has been observed to significantly increase decomposition of the biomass in slurry 5050. Typically, for example, a concentration of hydroxide ions in the alkaline solution is between 0.001% and 10% by weight of slurry 5050. After the feedstock has been wetted via contact with the alkaline solution, the ozone-containing gas is introduced into the oxidation reactor, where it contacts and oxidizes the feedstock.

Oxidizing agents 5160 can also include other substances. In some embodiments, for example, halogen-based oxidizing agents such as chlorine and oxychlorine agents (e.g., hypochlorite) can be introduced into slurry 5050. In certain embodiments, nitrogen-containing oxidizing substances can be introduced into slurry 5050. Exemplary nitrogen-containing oxidizing substances include NO and NO₂, for example. Nitrogen-containing agents can also be combined with oxygen in slurry 5050 to create additional oxidizing agents. For example, NO and NO₂ both combine with oxygen in slurry 5050 to form nitrate compounds, which are effective oxidizing agents for biomass feedstock. Halogen- and nitrogen-based oxidizing agents can, in some embodiments, cause bleaching of the biomass feedstock, depending upon the nature of the feedstock. The bleaching may be desirable for certain biomass-derived products that are extracted in subsequent processing steps.

Other oxidizing agents can include, for example, various peroxyacids, peroxyacetic acids, persulfates, percarbonates, permanganates, osmium tetroxide, and chromium oxides.

Following oxidation preprocessing step 5060, feedstock slurry 5050 is oxidized in step 5070. If oxidizing agents 5160 were added to slurry 5050 in an oxidation reactor, then oxidation proceeds in the same reactor. Alternatively, if oxidizing agents 5160 were added to slurry 5050 in a preprocessing chamber, then slurry 5050 is transported to an oxidation reactor via an in-line piping system. Once inside the oxidation reactor, oxidation of the biomass feedstock proceeds under a controlled set of environmental conditions. Typically, for example, the oxidation reactor is a cylindrical vessel that is closed to the external environment and pressurized. Both batch and continuous operation is possible, although environmental conditions are typically easier to control in in-line batch processing operations.

Oxidation of feedstock slurry 5050 typically occurs at elevated temperatures in the oxidation reactor. For example, the temperature of slurry 5050 in the oxidation reactor is typically maintained above 100° C., in a range from 120° C. to 240° C. For many types of biomass feedstock, oxidation is particularly efficient if the temperature of slurry 5050 is maintained between 150° C. and 220° C. Slurry 5050 can be heating using a variety of thermal transfer devices. For example, in some embodiments, the oxidation reactor contacts a heating bath that includes oil or molten salts. In certain embodiments, a series of heat exchange pipes surround and contact the oxidation reactor, and circulation of hot fluid within the pipes heats slurry 5050 in the reactor. Other heating devices that can be used to heat slurry 5050 include resistive heating elements, induction heaters, and microwave sources, for example.

The residence time of feedstock slurry 5050 in the oxidation reactor can be varied as desired to process the feedstock. Typically, slurry 5050 spends from 1 minute to 60 minutes undergoing oxidation in the reactor. For relatively soft biomass material such as lignocellulosic matter, the residence time in the oxidation reactor can be from 5 minutes to 30 minutes, for example, at an oxygen pressure of between 3 and 12 bars in the reactor, and at a slurry temperature of between 160° C. and 210° C. For other types of feedstock, however, residence times in the oxidation reactor can be longer, e.g., as long 48 hours. To determine appropriate residence times for slurry 5050 in the oxidation reactor, aliquots of the slurry can be extracted from the reactor at specific intervals and analyzed to determine concentrations of particular products of interest such as complex saccharides. Information about the increase in concentrations of certain products in slurry 5050 as a function of time can be used to determine residence times for particular classes of feedstock material.

In some embodiments, during oxidation of feedstock slurry 5050, adjustment of the slurry pH may be performed by introducing one or more chemical agents into the oxidation reactor. For example, in certain embodiments, oxidation occurs most efficiently in a pH range of about 9-11. To maintain a pH in this range, agents such as alkali and alkaline earth hydroxides, carbonates, ammonia, and alkaline buffer solutions can be introduced into the oxidation reactor.

Circulation of slurry 5050 during oxidation can be important to ensure sufficient contact between oxidizing agents 5160 and the feedstock. Circulation of the slurry can be achieved using a variety of techniques. For example, in some embodiments, a mechanical stirring apparatus that includes impeller blades or a paddle wheel can be implemented in the oxidation reactor. In certain embodiments, the oxidation reactor can be a loop reactor, in which the aqueous solvent in which the feedstock is suspended is simultaneously drained from the bottom of the reactor and recirculated into the top of the reactor via pumping, thereby ensuring that the slurry is continually re-mixed and does not stagnate within the reactor.

After oxidation of the feedstock is complete, the slurry is transported to a separation apparatus where a mechanical separation step 5080 occurs. Typically, mechanical separation step 5080 includes one or more stages of increasingly fine filtering of the slurry to mechanically separate the solid and liquid constituents.

Liquid phase 5090 is separated from solid phase 5100, and the two phases are processed independently thereafter. Solid phase 5100 can optionally undergo a drying step 5120 in a drying apparatus, for example. Drying step 5120 can include, for example, mechanically dispersing the solid material onto a drying surface, and evaporating water from solid phase 5100 by gentle heating of the solid material. Following drying step 5120 (or, alternatively, without undergoing drying step 5120), solid phase 5100 is transported for further processing steps 5140.

Liquid phase 5090 can optionally undergo a drying step 5110 to reduce the concentration of water in the liquid phase. In some embodiments, for example, drying step 5110 can include evaporation and/or distillation and/or extraction of water from liquid phase 5090 by gentle heating of the liquid. Alternatively, or in addition, one or more chemical drying agents can be used to remove water from liquid phase 5090. Following drying step 5110 (or alternatively, without undergoing drying step 5110), liquid phase 5090 is transported for further processing steps 5130, which can include a variety of chemical and biological treatment steps such as chemical and/or enzymatic hydrolysis.

Drying step 5110 creates waste stream 5220, an aqueous solution that can include dissolved chemical agents such as acids and bases in relatively low concentrations. Treatment of waste stream 5220 can include, for example, pH neutralization with one or more mineral acids or bases. Depending upon the concentration of dissolved salts in waste stream 5220, the solution may be partially de-ionized (e.g., by passing the waste stream through an ion exchange system). Then, the waste stream—which includes primarily water—can be re-circulated into the overall process (e.g., as water 5150), diverted to another process, or discharged.

Typically, for lignocellulosic biomass feedstocks following separation step 5070, liquid phase 5090 includes a variety of soluble poly- and oligosaccharides, which can then be separated and/or reduced to smaller-chain saccharides via further processing steps. Solid phase 5100 typically includes primarily cellulose, for example, with smaller amounts of hemicellulose- and lignin-derived products.

In some embodiments, oxidation can be carried out at elevated temperature in a reactor such as a pyrolysis chamber. For example, referring again to FIG. 17, feedstock materials can be oxidized in filament pyrolyzer 1712. In a typical usage, an oxidizing carrier gas, e.g., air or an air/argon blend, traverses through the sample holder 1713 while the resistive heating element is rotated and heated to a desired temperature, e.g., 325° C. After an appropriate time, e.g., 5 to 10 minutes, the oxidized material is emptied from the sample holder. The system shown in FIG. 17 can be scaled and made continuous. For example, rather than a wire as the heating member, the heating member can be an auger screw. Material can continuously fall into the sample holder, striking a heated screw that pyrolizes the material. At the same time, the screw can push the oxidized material out of the sample holder to allow for the entry of fresh, unoxidized material.

Feedstock materials can also be oxidized in any of the pyrolysis systems shown in FIGS. 18-20 and described above in the Pyrolysis Systems section.

Referring again to FIG. 21, feedstock materials can be rapidly oxidized by coating a tungsten filament 150, together with an oxidant, such as a peroxide, with the desired cellulosic material while the material is housed in a vacuum chamber 151. To affect oxidation, current is passed through the filament, which causes a rapid heating of the filament for a desired time. Typically, the heating is continued for seconds before allowing the filament to cool. In some embodiments, the heating is performed a number of times to effect the desired amount of oxidation.

Referring again to FIG. 12, in some embodiments, feedstock materials can be oxidized with the aid of sound and/or cavitation. Generally, to effect oxidation, the materials are sonicated in an oxidizing environment, such as water saturated with oxygen or another chemical oxidant, such as hydrogen peroxide.

Referring again to FIGS. 9 and 10, in certain embodiments, ionizing radiation is used to aid in the oxidation of feedstock materials. Generally, to effect oxidation, the materials are irradiated in an oxidizing environment, such as air or oxygen. For example, gamma radiation and/or electron beam radiation can be employed to irradiate the materials.

Other Processes

Steam explosion can be used alone without any of the processes described herein, or in combination with any of the processes described herein.

FIG. 23 shows an overview of the entire process of converting a fiber source 400 into a product 450, such as ethanol, by a process that includes shearing and steam explosion to produce a fibrous material 401, which is then hydrolyzed and converted, e.g., fermented, to produce the product. The fiber source can be transformed into the fibrous material 401 through a number of possible methods, including at least one shearing process and at least one steam explosion process.

For example, one option includes shearing the fiber source, followed by optional screening step(s) and optional additional shearing step(s) to produce a sheared fiber source 402, which can then be steam exploded to produce the fibrous material 401. The steam explosion process is optionally followed by a fiber recovery process to remove liquids or the “liquor” 404, resulting from the steam exploding process. The material resulting from steam exploding the sheared fiber source may be further sheared by optional additional shearing step(s) and/or optional screening step(s).

In another method, the fibrous material 401 is first steam exploded to produce a steam exploded fiber source 410. The resulting steam exploded fiber source is then subjected to an optional fiber recovery process to remove liquids, or the liquor. The resulting steam exploded fiber source can then be sheared to produce the fibrous material. The steam exploded fiber source can also be subject to one or more optional screening steps and/or one or more optional additional shearing steps. The process of shearing and steam exploding the fiber source to produce the sheared and steam exploded fibrous material will be further discussed below.

The fiber source can be cut into pieces or strips of confetti material prior to shearing or steam explosion. The shearing processes can take place with the material in a dry state (e.g., having less than 0.25 percent by weight absorbed water), a hydrated state, or even while the material is partially or fully submerged in a liquid, such as water or isopropanol. The process can also optimally include steps of drying the output after steam exploding or shearing to allow for additional steps of dry shearing or steam exploding. The steps of shearing, screening, and steam explosion can take place with or without the presence of various chemical solutions.

In a steam explosion process, the fiber source or the sheared fiber source is contacted with steam under high pressure, and the steam diffuses into the structures of the fiber source (e.g., the lignocellulosic structures). The steam then condenses under high pressure thereby “wetting” the fiber source. The moisture in the fiber source can hydrolyze any acetyl groups in the fiber source (e.g., the acetyl groups in the hemicellulose fractions), forming organic acids such as acetic and uronic acids. The acids, in turn, can catalyze the depolymerization of hemicellulose, releasing xylan and limited amounts of glucan. The “wet” fiber source (or sheared fiber source, etc.) is then “exploded” when the pressure is released. The condensed moisture instantaneously evaporates due to the sudden decrease in pressure and the expansion of the water vapor exerts a shear force upon the fiber source (or sheared fiber source, etc.). A sufficient shear force will cause the mechanical breakdown of the internal structures (e.g., the lignocellulosic structures) of the fiber source.

The sheared and steam exploded fibrous material is then converted into a useful product, such as ethanol. In some embodiments, the fibrous material is converted into a fuel. One method of converting the fibrous material into a fuel is by hydrolysis to produce fermentable sugars, 412, which are then fermented to produce the product. Other known and unknown methods of converting fibrous materials into fuels may also be used.

In some embodiments, prior to combining the microorganism, the sheared and steam exploded fibrous material 401 is sterilized to kill any competing microorganisms that may be on the fibrous material. For example, the fibrous material can be sterilized by exposing the fibrous material to radiation, such as infrared radiation, ultraviolet radiation, or an ionizing radiation, such as gamma radiation. The microorganisms can also be killed using chemical sterilants, such as bleach (e.g., sodium hypochlorite), chlorhexidine, or ethylene oxide.

One method to hydrolyze the sheared and steam exploded fibrous material is by the use of cellulases. Cellulases are a group of enzymes that act synergistically to hydrolyze cellulose. Commercially available Accellerase® 1000 enzyme complex, which contains a complex of enzymes that reduces lignocellulosic biomass into fermentable sugars, can also be used.

According to current understanding, the components of cellulase include endoglucanases, exoglucanases (cellobiohydrolases), and b-glucosidases (cellobiases). Synergism between the cellulase components exists when hydrolysis by a combination of two or more components exceeds the sum of the activities expressed by the individual components. The generally accepted mechanism of a cellulase system (particularly of T. longibrachiatum) on crystalline cellulose is: endoglucanase hydrolyzes internal 0-1,4-glycosidic bonds of the amorphous regions, thereby increasing the number of exposed non-reducing ends. Exoglucanases then cleave off cellobiose units from the nonreducing ends, which in turn are hydrolyzed to individual glucose units by b-glucosidases. There are several configurations of both endo- and exo-glucanases differing in stereo specificities. In general, the synergistic action of the components in various configurations is required for optimum cellulose hydrolysis. Cellulases, however, are more inclined to hydrolyze the amorphous regions of cellulose. A linear relationship between crystallinity and hydrolysis rates exists whereby higher crystallinity indices correspond to slower enzyme hydrolysis rates. Amorphous regions of cellulose hydrolyze at twice the rate of crystalline regions. The hydrolysis of the sheared and steam exploded fibrous material may be performed by any hydrolyzing biomass process.

Steam explosion of biomass sometimes causes the formation of by-products, e.g., toxicants, that are inhibitory to microbial and enzymatic activities. The process of converting the sheared and steam exploded fibrous material into a fuel can therefore optionally include an overliming step prior to fermentation to precipitate some of the toxicants. For example, the pH of the sheared and steam exploded fibrous material may be raised to exceed the pH of 10 by adding calcium hydroxide (Ca(OH)₂) followed by a step of lowering the pH to about 5 by adding H₂SO₄. The overlimed fibrous material may then be used as is without the removal of precipitates. As shown in FIG. 23, the optional overliming step occurs just prior to the step of hydrolysis of the sheared and steam exploded fibrous material, but it is also contemplated to perform the overliming step after the hydrolysis step and prior to the fermenting step.

FIG. 24 depicts an example of a steam explosion apparatus 460. The steam explosion apparatus 460 includes a reaction chamber 462, in which the fiber source and/or the fibrous material is placed through a fiber source inlet 464. Closing fiber source inlet valve 465 seals the reaction chamber. The reaction chamber further includes a pressurized steam inlet 466 that includes a steam valve 467. The reaction chamber further includes an explosive depressurization outlet 468 that includes an outlet valve 469 in communication with the cyclone 470 through the connecting pipe 472. Once the reaction chamber contains the fiber source and/or sheared fiber source and is sealed by closing valves 465, 467 and 469, steam is delivered into the reaction chamber 462 by opening the steam inlet valve 467 allowing steam to travel through steam inlet 466. Once the reaction chamber reaches target temperature, which can take about 20-60 seconds, the holding time begins. The reaction chamber is held at the target temperature for the desired holding time, which typically lasts from about 10 seconds to 5 minutes. At the end of the holding time period, outlet valve is opened to allow for explosive depressurization to occur. The process of explosive depressurization propels the contents of the reaction chamber 462 out of the explosive depressurization outlet 468, through the connecting pipe 472, and into the cyclone 470. The steam exploded fiber source or fibrous material then exits the cyclone in a sludge form into the collection bin 474 as much of the remaining steam exits the cyclone into the atmosphere through vent 476. The steam explosion apparatus further includes wash outlet 478 with wash outlet valve 479 in communication with connecting pipe 472. The wash outlet valve 479 is closed during the use of the steam explosion apparatus 460 for steam explosion, but opened during the washing of the reaction chamber 462.

The target temperature of the reaction chamber 462 is preferably between 180 and 240 degrees Celsius or between 200 and 220 degrees Celsius. The holding time is preferably between 10 seconds and 30 minutes, or between 30 seconds and 10 minutes, or between 1 minute and 5 minutes.

Because the steam explosion process results in a sludge of steam exploded fibrous material, the steam exploded fibrous material may optionally include a fiber recovery process where the “liquor” is separated from the steam exploded fibrous material. This fiber recovery step is helpful in that it enables further shearing and/or screening processes and can allow for the conversion of the fibrous material into fuel. The fiber recovery process occurs through the use of a mesh cloth to separate the fibers from the liquor. Further drying processes can also be included to prepare the fibrous material or steam exploded fiber source for subsequent processing.

Combined Irradiating, Pyrolyzing, Sonicating, and/or Oxidizing Devices

In some embodiments, it may be advantageous to combine two or more separate irradiation, sonication, pyrolyzation, and/or oxidation devices into a single hybrid machine. Using such a hybrid machine, multiple processes may be performed in close juxtaposition or even simultaneously, with the benefit of increasing pretreatment throughput and potential cost savings.

For example, consider the electron beam irradiation and sonication processes. Each separate process is effective in lowering the mean molecular weight of cellulosic material by an order of magnitude or more, and by several orders of magnitude when performed serially.

Both irradiation and sonication processes can be applied using a hybrid electron beam/sonication device as is illustrated in FIG. 25. Hybrid electron beam/sonication device 2500 is pictured above a shallow pool (depth ˜3-5 cm) of a slurry of cellulosic material 2550 dispersed in an aqueous, oxidant medium, such as hydrogen peroxide or carbamide peroxide. Hybrid device 2500 has an energy source 2510, which powers both electron beam emitter 2540 and sonication horns 2530.

Electron beam emitter 2540 generates electron beams, which pass though an electron beam aiming device 2545 to impact the slurry 2550 containing cellulosic material. The electron beam-aiming device can be a scanner that sweeps a beam over a range of up to about 6 feet in a direction approximately parallel to the surface of the slurry 2550.

On either side of the electron beam emitter 2540 are sonication horns 2530, which deliver ultrasonic wave energy to the slurry 2550. The sonication horns 2530 end in a detachable endpiece 2535 that is in contact with the slurry 2550.

The sonication horns 2530 are at risk of damage from long-term residual exposure to the electron beam radiation. Thus, the horns can be protected with a standard shield 2520, e.g., made of lead or a heavy-metal-containing alloy such as Lipowitz metal, which is impervious to electron beam radiation. Precautions must be taken, however, to ensure that the ultrasonic energy is not affected by the presence of the shield. The detachable endpieces 2535, which are constructed of the same material and attached to the horns 2530, are in contact with the cellulosic material 2550 during processing and are expected to be damaged. Accordingly, the detachable endpieces 2535 are constructed to be easily replaceable.

A further benefit of such a simultaneous electron beam and ultrasound process is that the two processes have complementary results. With electron beam irradiation alone, an insufficient dose may result in cross-linking of some of the polymers in the cellulosic material, which lowers the efficiency of the overall depolymerization process. Lower doses of electron beam irradiation and/or ultrasound radiation may also be used to achieve a similar degree of depolymerization as that achieved using electron beam irradiation and sonication separately. An electron beam device can also be combined with one or more of high-frequency, rotor-stator devices, which can be used as an alternative to ultrasonic sonication devices.

Further combinations of devices are also possible. For example, an ionizing radiation device that produces gamma radiation emitted from, e.g., ⁶⁰Co pellets, can be combined with an electron beam source and/or an ultrasonic wave source. Shielding requirements may be more stringent in this case.

The radiation devices for pretreating biomass discussed above can also be combined with one or more devices that perform one or more pyrolysis processing sequences. Such a combination may again have the advantage of higher throughput. Nevertheless, caution must be observed, as there may be conflicting requirements between some radiation processes and pyrolysis. For example, ultrasonic radiation devices may require the feedstock be immersed in a liquid oxidizing medium. On the other hand, as discussed previously, it may be advantageous for a sample of feedstock undergoing pyrolysis to be of a particular moisture content. In this case, the new systems automatically measure and monitor for a particular moisture content and regulate the same Further, some or all of the above devices, especially the pyrolysis device, can be combined with an oxidation device as discussed previously.

Primary Processes Fermentation

Generally, various microorganisms can produce a number of useful products, such as a fuel, by operating on, e.g., fermenting the pretreated biomass materials. For example, fermentation or other processes can produce alcohols, organic acids, hydrocarbons, hydrogen, proteins or mixtures of any of these materials.

The microorganism can be a natural microorganism or an engineered microorganism. For example, the microorganism can be a bacterium, e.g., a cellulolytic bacterium, a fungus, e.g., a yeast, a plant or a protist, e.g., an algae, a protozoa or a fungus-like protist, e.g., a slime mold. When the organisms are compatible, mixtures of organisms can be utilized.

To aid in the breakdown of the materials that include the cellulose, one or more enzymes, e.g., a cellulolytic enzyme can be utilized. In some embodiments, the materials that include the cellulose are first treated with the enzyme, e.g., by combining the material and the enzyme in an aqueous solution. This material can then be combined with the microorganism. In other embodiments, the materials that include the cellulose, the one or more enzymes and the microorganism are combined at the concurrently, e.g., by combining in an aqueous solution.

Also, to aid in the breakdown of the materials that include the cellulose, the materials can be treated post irradiation with heat, a chemical (e.g., mineral acid, base or a strong oxidizer such as sodium hypochlorite), and/or an enzyme.

During the fermentation, sugars released from cellulolytic hydrolysis or the saccharification step, are fermented to, e.g., ethanol, by a fermenting microorganism such as yeast. Suitable fermenting microorganisms have the ability to convert carbohydrates, such as glucose, xylose, arabinose, mannose, galactose, oligosaccharides or polysaccharides into fermentation products. Fermenting microorganisms include strains of the genus Sacchromyces spp. e.g., Sacchromyces cerevisiae (baker's yeast), Saccharomyces distaticus, Saccharomyces uvarum; the genus Kluyveromyces, e.g., species Kluyveromyces marxianus, Kluyveromyces fragilis; the genus Candida, e.g., Candida pseudotropicalis, and Candida brassicae, Pichia stipitis (a relative of Candida shehatae, the genus Clavispora, e.g., species Clavispora lusitaniae and Clavispora opuntiae the genus Pachysolen, e.g., species Pachysolen tannophilus, the genus Bretannomyces, e.g., species Bretannomyces clausenji (Philippidis, G. P., 1996, Cellulose bioconversion technology, in Handbook on Bioethanol: Production and Utilization, Wyman, C. E., ed., Taylor & Francis, Washington, D.C., 179-212).

Commercially available yeast include, for example, Red Star®/Lesaffre Ethanol Red (available from Red Star/Lesaffre, USA) FALI® (available from Fleischmann's Yeast, a division of Burns Philip Food Inc., USA), SUPERSTART® (available from Alltech), GERT STRAND® (available from Gert Strand AB, Sweden) and FERMOL® (available from DSM Specialties).

Bacteria that can ferment biomass to ethanol and other products include, e.g., Zymomonas mobilis and Clostridium thermocellum (Philippidis, 1996, supra). Leschine et al. (International Journal of Systematic and Evolutionary Microbiology 2002, 52, 1155-1160) isolated an anaerobic, mesophilic, cellulolytic bacterium from forest soil, Clostridium phytofermentans sp. nov., which converts cellulose to ethanol.

Fermentation of biomass to ethanol and other products may be carried out using certain types of thermophilic or genetically engineered microorganisms, such Thermoanaerobacter species, including T. mathranii, and yeast species such as Pichia species. An example of a strain of T. mathranii is A3M4 described in Sonne-Hansen et al. (Applied Microbiology and Biotechnology 1993, 38, 537-541) or Ahring et al. (Arch. Microbiol. 1997, 168, 114-119).

Yeast and Zymomonas bacteria can be used for fermentation or conversion. The optimum pH for yeast is from about pH 4 to 5, while the optimum pH for Zymomonas is from about pH 5 to 6. Typical fermentation times are about 24 to 96 hours with temperatures in the range of 26° C. to 40° C., however thermophilic microorganisms prefer higher temperatures.

Enzymes which break down biomass, such as cellulose, to lower molecular weight carbohydrate-containing materials, such as glucose, during saccharification are referred to as cellulolytic enzymes or cellulase. These enzymes may be a complex of enzymes that act synergistically to degrade crystalline cellulose. Examples of cellulolytic enzymes include: endoglucanases, cellobiohydrolases, and cellobiases (β-glucosidases). A cellulosic substrate is initially hydrolyzed by endoglucanases at random locations producing oligomeric intermediates. These intermediates are then substrates for exo-splitting glucanases such as cellobiohydrolase to produce cellobiose from the ends of the cellulose polymer. Cellobiose is a water-soluble β-1,4-linked dimer of glucose. Finally cellobiase cleaves cellobiose to yield glucose.

A cellulase is capable of degrading biomass and may be of fungal or bacterial origin. Suitable enzymes include cellulases from the genera Bacillus, Pseudomonas, Humicola, Fusarium, Thielavia, Acremonium, Chrysosporium and Trichoderma, and include species of Humicola, Coprinus, Thielavia, Fusarium, Myceliophthora, Acremonium, Cephalosporium, Scytalidium, Penicillium or Aspergillus (see, e.g., EP 458162), especially those produced by a strain selected from the species Humicola insolens (reclassified as Scytalidium thermophilum, see, e.g., U.S. Pat. No. 4,435,307), Coprinus cinereus, Fusarium oxysporum, Myceliophthora thermophila, Meripilus giganteus, Thielavia terrestris, Acremonium sp., Acremonium persicinum, Acremonium acremonium, Acremonium brachypenium, Acremonium dichromosporum, Acremonium obclavatum, Acremonium pinkertoniae, Acremonium roseogriseum, Acremonium incoloratum, and Acremoniumfuratum; preferably from the species Humicola insolens DSM 1800, Fusarium oxysporum DSM 2672, Myceliophthora thermophila CBS117.65, Cephalosporium sp. RYM-202, Acremonium sp. CBS 478.94, Acremonium sp. CBS 265.95, Acremonium persicinum CBS169.65, Acremonium acremonium AHU 9519, Cephalosporium sp. CBS 535.71, Acremonium brachypenium CBS 866.73, Acremonium dichromosporum CBS 683.73, Acremonium obclavatum CBS 311.74, Acremonium pinkertoniae CBS157.70, Acremonium roseogriseum CBS134.56, Acremonium incoloratum CBS146.62, and Acremonium furatum CBS 299.70H. Cellulolytic enzymes may also be obtained from Chrysosporiu™, preferably a strain of Chrysosporium lucknowense. Additionally, Trichoderma (particularly Trichoderma viride, Trichoderma reesei, and Trichoderma koningii), alkalophilic Bacillus (see, for example, U.S. Pat. No. 3,844,890 and EP 458162), and Streptomyces (see, e.g., EP 458162) may be used. The bacterium, Saccharophagus degradans, produces a mixture of enzymes capable of degrading a range of cellulosic materials and may also be used in this process.

Anaerobic cellulolytic bacteria have also been isolated from soil, e.g., a novel cellulolytic species of Clostiridium, Clostridium phytofermentans sp. nov. (see Leschine et. al, International Journal of Systematic and Evolutionary Microbiology (2002), 52, 1155-1160).

Cellulolytic enzymes using recombinant technology can also be used (see, e.g., WO 2007/071818 and WO 2006/110891).

The cellulolytic enzymes used can be produced by fermentation of the above-noted microbial strains on a nutrient medium containing suitable carbon and nitrogen sources and inorganic salts, using procedures known in the art (see, e.g., Bennett, J. W. and LaSure, L. (eds.), More Gene Manipulations in Fungi, Academic Press, CA 1991). Suitable media are available from commercial suppliers or may be prepared according to published compositions (e.g., in catalogues of the American Type Culture Collection). Temperature ranges and other conditions suitable for growth and cellulase production are known in the art (see, e.g., Bailey, J. E., and Ollis, D. F., Biochemical Engineering Fundamentals, McGraw-Hill Book Company, NY, 1986).

Treatment of cellulose with cellulase is usually carried out at temperatures between 30° C. and 65° C. Cellulases are active over a range of pH of about 3 to 7. A saccharification step may last up to 120 hours. The cellulase enzyme dosage achieves a sufficiently high level of cellulose conversion. For example, an appropriate cellulase dosage is typically between 5.0 and 50 Filter Paper Units (FPU or IU) per gram of cellulose. The FPU is a standard measurement and is defined and measured according to Ghose (1987, Pure and Appl. Chem. 59:257-268).

Mobile fermentors can be utilized, as described in U.S. Provisional Patent Application Ser. 60/832,735, now Published International Application No. WO 2008/011598.

Gasification

In addition to using pyrolysis for pre-treatment of feedstock, pyrolysis can also be used to process pre-treated feedstock to extract useful materials. In particular, a form of pyrolysis known as gasification can be employed to generate fuel gases along with various other gaseous, liquid, and solid products. To perform gasification, the pre-treated feedstock is introduced into a pyrolysis chamber and heated to a high temperature, typically 700° C. or more. The temperature used depends upon a number of factors, including the nature of the feedstock and the desired products.

Quantities of oxygen (e.g., as pure oxygen gas and/or as air) and steam (e.g., superheated steam) are also added to the pyrolysis chamber to facilitate gasification. These compounds react with carbon-containing feedstock material in a multiple-step reaction to generate a gas mixture called synthesis gas (or “syngas”). Essentially, during gasification, a limited amount of oxygen is introduced into the pyrolysis chamber to allow some feedstock material to combust to form carbon monoxide and generate process heat. The process heat can then be used to promote a second reaction that converts additional feedstock material to hydrogen and carbon monoxide.

In a first step of the overall reaction, heating the feedstock material produces a char that can include a wide variety of different hydrocarbon-based species. Certain volatile materials can be produced (e.g., certain gaseous hydrocarbon materials), resulting in a reduction of the overall weight of the feedstock material. Then, in a second step of the reaction, some of the volatile material that is produced in the first step reacts with oxygen in a combustion reaction to produce both carbon monoxide and carbon dioxide. The combustion reaction releases heat, which promotes the third step of the reaction. In the third step, carbon dioxide and steam (e.g., water) react with the char generated in the first step to form carbon monoxide and hydrogen gas. Carbon monoxide can also react with steam, in a water gas shift reaction, to form carbon dioxide and further hydrogen gas.

Gasification can be used as a primary process to generate products directly from pre-treated feedstock for subsequent transport and/or sale, for example. Alternatively, or in addition, gasification can be used as an auxiliary process for generating fuel for an overall processing system. The hydrogen-rich syngas that is generated via the gasification process can be burned, for example, to generate electricity and/or process heat that can be directed for use at other locations in the processing system. As a result, the overall processing system can be at least partially self-sustaining. A number of other products, including pyrolysis oils and gaseous hydrocarbon-based substances, can also be obtained during and/or following gasification; these can be separated and stored or transported as desired.

A variety of different pyrolysis chambers are suitable for gasification of pre-treated feedstock, including the pyrolysis chambers disclosed herein. In particular, fluidized bed reactor systems, in which the pre-treated feedstock is fluidized in steam and oxygen/air, provide relatively high throughput and straightforward recovery of products. Solid char that remains following gasification in a fluidized bed system (or in other pyrolysis chambers) can be burned to generate additional process heat to promote subsequent gasification reactions.

Post-Processing Distillation

After fermentation, the resulting fluids can be distilled using, for example, a “beer column” to separate ethanol and other alcohols from the majority of water and residual solids. The vapor exiting the beer column can be, e.g., 35% by weight ethanol and can be fed to a rectification column. A mixture of nearly azeotropic (92.5%) ethanol and water from the rectification column can be purified to pure (99.5%) ethanol using vapor-phase molecular sieves. The beer column bottoms can be sent to the first effect of a three-effect evaporator. The rectification column reflux condenser can provide heat for this first effect. After the first effect, solids can be separated using a centrifuge and dried in a rotary dryer. A portion (25%) of the centrifuge effluent can be recycled to fermentation and the rest sent to the second and third evaporator effects. Most of the evaporator condensate can be returned to the process as fairly clean condensate with a small portion split off to waste water treatment to prevent build-up of low-boiling compounds.

Waste Water Treatment

Wastewater treatment is used to minimize makeup water requirements of the plant by treating process water for reuse within the plant. Wastewater treatment can also produce fuel (e.g., sludge and biogas) that can be used to improve the overall efficiency of the ethanol production process. For example, as described in further detail below, sludge and biogas can be used to create steam and electricity that can be used in various plant processes.

Wastewater is initially pumped through a screen (e.g., a bar screen) to remove large particles, which are collected in a hopper. In some embodiments, the large particles are sent to a landfill. Additionally or alternatively, the large particles are burned to create steam and/or electricity as described in further detail below. In general, the spacing on the bar screen is between ¼ inch to 1 inch spacing (e.g., ½ inch spacing).

The wastewater then flows to an equalization tank, where the organic concentration of the wastewater is equalized during a retention time. In general, the retention time is between 8 hours and 36 hours (e.g., 24 hours). A mixer is disposed within the tank to stir the contents of the tank. In some embodiments, a plurality of mixers disposed throughout the tank are used to stir the contents of the tank. In certain embodiments, the mixer substantially mixes the contents of the equalization tank such that conditions (e.g., wastewater concentration and temperature) throughout the tank are uniform.

A first pump moves water from the equalization tank through a liquid-to-liquid heat exchanger. The heat exchanger is controlled (e.g., by controlling the flow rate of fluid through the heat exchanger) such that wastewater exiting the heat exchanger is at a desired temperature for anaerobic treatment. For example, the desired temperature for anaerobic treatment can be between 40° C. to 60° C.

After exiting the heat exchanger, the wastewater enters one or more anaerobic reactors. In some embodiments, the concentration of sludge in each anaerobic reactor is the same as the overall concentration of sludge in the wastewater. In other embodiments, the anaerobic reactor has a higher concentration of sludge than the overall concentration of sludge in the wastewater.

A nutrient solution containing nitrogen and phosphorus is metered into each anaerobic reactor containing wastewater. The nutrient solution reacts with the sludge in the anaerobic reactor to produce biogas which can contain 50% methane and have a heating value of approximately 12,000 British thermal units, or Btu, per pound). The biogas exits each anaerobic reactor through a vent and flows into a manifold, where a plurality of biogas streams are combined into a single stream. A compressor moves the stream of biogas to a boiler or a combustion engine as described in further detail below. In some embodiments, the compressor also moves the single stream of biogas through a desulphurization catalyst. Additionally or alternatively, the compressor can move the single stream of biogas through a sediment trap.

A second pump moves anaerobic effluent from the anaerobic reactors to one or more aerobic reactors (e.g., activated sludge reactors). An aerator is disposed within each aerobic reactor to mix the anaerobic effluent, sludge, and oxygen (e.g., oxygen contained in air). Within each aerobic reactor, oxidation of cellular material in the anaerobic effluent produces carbon dioxide, water, and ammonia.

Aerobic effluent moves (e.g., via gravity) to a separator, where sludge is separated from treated water. Some of the sludge is returned to the one or more aerobic reactors to create an elevated sludge concentration in the aerobic reactors, thereby facilitating the aerobic breakdown of cellular material in the wastewater. A conveyor removes excess sludge from the separator. As described in further detail below, the excess sludge is used as fuel to create steam and/or electricity.

The treated water is pumped from the separator to a settling tank. Solids dispersed throughout the treated water settle to the bottom of the settling tank and are subsequently removed. After a settling period, treated water is pumped from the settling tank through a fine filter to remove any additional solids remaining in the water. In some embodiments, chlorine is added to the treated water to kill pathogenic bacteria. In some embodiments, one or more physical-chemical separation techniques are used to further purify the treated water. For example, treated water can be pumped through a carbon adsorption reactor. As another example, treated water can pumped through a reverse osmosis reactor.

In the processes disclosed herein, whenever water is used in any process, it may be grey water, e.g., municipal grey water, or black water. In some embodiments, the grey or black water is sterilized prior to use. Sterilization may be accomplished by any desired technique, for example by irradiation, steam, or chemical sterilization.

Waste Combustion

The production of alcohol from biomass can result in the production of various by-product streams useful for generating steam and electricity to be used in other parts of the plant. For example, steam generated from burning by-product streams can be used in the distillation process. As another example, electricity generated from burning by-product streams can be used to power electron beam generators and ultrasonic transducers used in pretreatment.

The by-products used to generate steam and electricity are derived from a number of sources throughout the process. For example, anaerobic digestion of wastewater produces a biogas high in methane and a small amount of waste biomass (sludge). As another example, post-distillate solids (e.g., unconverted lignin, cellulose, and hemicellulose remaining from the pretreatment and primary processes) can be used as a fuel.

The biogas is diverted to a combustion engine connected to an electric generator to produce electricity. For example, the biogas can be used as a fuel source for a spark-ignited natural gas engine. As another example, the biogas can be used as a fuel source for a direct-injection natural gas engine. As another example, the biogas can be used as a fuel source for a combustion turbine. Additionally or alternatively, the combustion engine can be configured in a cogeneration configuration. For example, waste heat from the combustion engines can be used to provide hot water or steam throughout the plant.

The sludge, and post-distillate solids are burned to heat water flowing through a heat exchanger. In some embodiments, the water flowing through the heat exchanger is evaporated and superheated to steam. In certain embodiments, the steam is used in the pretreatment rector and in heat exchange in the distillation and evaporation processes. Additionally or alternatively, the steam expands to power a multi-stage steam turbine connected to an electric generator. Steam exiting the steam turbine is condensed with cooling water and returned to the heat exchanger for reheating to steam. In some embodiments, the flow rate of water through the heat exchanger is controlled to obtain a target electricity output from the steam turbine connected to an electric generator. For example, water can be added to the heat exchanger to ensure that the steam turbine is operating above a threshold condition (e.g., the turbine is spinning fast enough to turn the electric generator).

While certain embodiments have been described, other embodiments are possible.

As an example, while the biogas is described as being diverted to a combustion engine connected to an electric generator, in certain embodiments, the biogas can be passed through a fuel reformer to produce hydrogen. The hydrogen is then converted to electricity through a fuel cell.

As another example, while the biogas is described as being burned apart from the sludge and post-distillate solids, in certain embodiments, all of the waste by-products can be burned together to produce steam.

Products/Co-Products Alcohols

The alcohol produced can be a monohydroxy alcohol, e.g., ethanol, or a polyhydroxy alcohol, e.g., ethylene glycol or glycerin. Examples of alcohols that can be produced include methanol, ethanol, propanol, isopropanol, butanol, e.g., n-, sec- or t-butanol, ethylene glycol, propylene glycol, 1,4-butane diol, glycerin or mixtures of these alcohols.

Each of the alcohols produced by the plant have commercial value as industrial feedstock. For example, ethanol can be used in the manufacture of varnishes and perfume. As another example, methanol can be used as a solvent used as a component in windshield wiper fluid. As still another example, butanol can be used in plasticizers, resins, lacquers, and brake fluids.

Bioethanol produced by the plant is valuable as an ingredient used in the food and beverage industry. For example, the ethanol produced by the plant can be purified to food grade alcohol and used as a primary ingredient in the alcoholic beverages.

Bioethanol produced by the plant also has commercial value as a transportation fuel. The use of ethanol as a transportation fuel can be implemented with relatively little capital investment from spark ignition engine manufacturers and owners (e.g., changes to injection timing, fuel-to-air ratio, and components of the fuel injection system). Many automotive manufacturers currently offer flex-fuel vehicles capable of operation on ethanol/gasoline blends up to 85% ethanol by volume (e.g., standard equipment on a Chevy Tahoe 4×4).

Bioethanol produced by this plant can be used as an engine fuel to improve environmental and economic conditions beyond the location of the plant. For example, ethanol produced by this plant and used as a fuel can reduce greenhouse gas emissions from manmade sources (e.g., transportation sources). As another example, ethanol produced by this plant and used as an engine fuel can also displace consumption of gasoline refined from oil.

Bioethanol has a greater octane number than conventional gasoline and, thus, can be used to improve the performance (e.g., allow for higher compression ratios) of spark ignition engines. For example, small amounts (e.g., 10% by volume) of ethanol can be blended with gasoline to act as an octane enhancer for fuels used in spark ignition engines. As another example, larger amounts (e.g., 85% by volume) of ethanol can be blended with gasoline to further increase the fuel octane number and displace larger volumes of gasoline.

Bioethanol strategies are discussed, e.g., by DiPardo in Journal of Outlook for Biomass Ethanol Production and Demand (EIA Forecasts), 2002; Sheehan in Biotechnology Progress, 15:8179, 1999; Martin in Enzyme Microbes Technology, 31:274, 2002; Greer in BioCycle, 61-65, April 2005; Lynd in Microbiology and Molecular Biology Reviews, 66:3, 506-577, 2002; Ljungdahl et al. in U.S. Pat. No. 4,292,406; and Bellamy in U.S. Pat. No. 4,094,742.

Organic Acids

The organic acids produced can include monocarboxylic acids or polycarboxylic acids. Examples of organic acids include formic acid, acetic acid, propionic acid, butyric acid, valeric acid, caproic, palmitic acid, stearic acid, oxalic acid, malonic acid, succinic acid, glutaric acid, oleic acid, linoleic acid, glycolic acid, lactic acid, γ-hydroxybutyric acid or mixtures of these acids.

Food Products

In some embodiments, all or a portion of the fermentation process can be interrupted before the cellulosic material is completely converted to ethanol. The intermediate fermentation products include high concentrations of sugar and carbohydrates. These intermediate fermentation products can be used in preparation of food for human or animal consumption. In some embodiments, irradiation pretreatment of the cellulosic material will render the intermediate fermentation products sterile (e.g., fit for human consumption). In some embodiments, the intermediate fermentation products will require post-processing prior to use as food. For example, a dryer can be used to remove moisture from the intermediate fermentation products to facilitate storage, handling, and shelf life. Additionally or alternatively, the intermediate fermentation products can be ground to a fine particle size in a stainless-steel laboratory mill to produce a flour-like substance.

Animal Feed

Distillers grains and solubles can be converted into a valuable byproduct of the distillation-dehydration process. After the distillation-dehydration process, distillers grains and solubles can be dried to improve the ability to store and handle the material. The resulting dried distillers grains and solubles (DDGS) is low in starch, high in fat, high in protein, high in fiber, and high in phosphorous. Thus, for example, DDGS can be valuable as a source of animal feed (e.g., as a feed source for dairy cattle). DDGS can be subsequently combined with nutritional additives to meet specific dietary requirements of specific categories of animals (e.g., balancing digestible lysine and phosphorus for swine diets).

Pharmaceuticals

The pretreatment processes discussed above can be applied to plants with medicinal properties. In some embodiments, sonication can stimulate bioactivity and/or bioavailabilty of the medicinal components of plants with medicinal properties. Additionally or alternatively, irradiation stimulates bioactivity and/or bioavailabilty of the medicinal components of plants with medicinal properties. For example, sonication and irradiation can be combined in the pretreatment of willow bark to stimulate the production of salicin.

Nutriceuticals

In some embodiments, intermediate fermentation products (e.g., products that include high concentrations of sugar and carbohydrates) can be supplemented to create a nutriceutical. For example, intermediate fermentation products can be supplemented with calcium to create a nutriceutical that provides energy and helps improve or maintain bone strength.

Co-Products Lignin Residue

As described above, lignin-containing residues from primary and pretreatment processes has value as a high/medium energy fuel and can be used to generate power and steam for use in plant processes. However, such lignin residues are a new type of solids fuel and there is little demand for it outside of the plant boundaries, and the costs of drying it for transportation only subtract from its potential value. In some cases, gasification of the lignin residues can convert it to a higher-value product with lower cost.

Other Co-Products

Cell matter, furfural, and acetic acid have been identified as potential co-products of biomass-to-fuel processing facilities. Interstitial cell matter could be valuable, but might require significant purification. Markets for furfural and acetic acid are in place, although it is unlikely that they are large enough to consume the output of a fully commercialized lignocellulose-to-ethanol industry.

EXAMPLES

The following Examples are intended to illustrate, and do not limit the teachings of this disclosure.

Example 1 Preparation of Fibrous Material from Polycoated Paper

A 1500 pound skid of virgin, half-gallon juice cartons made of un-printed polycoated white Kraft board having a bulk density of 201b/ft³ was obtained from International Paper. Each carton was folded flat, and then fed into a 3 hp Flinch Baugh shredder at a rate of approximately 15 to 20 pounds per hour. The shredder was equipped with two 12 inch rotary blades, two fixed blades and a 0.30 inch discharge screen. The gap between the rotary and fixed blades was adjusted to 0.10 inch. The output from the shredder resembled confetti having a width of between 0.1 inch and 0.5 inch, a length of between 0.25 inch and 1 inch and a thickness equivalent to that of the starting material (about 0.075 inch).

The confetti-like material was fed to a Munson rotary knife cutter, Model SC30. Model SC30 is equipped with four rotary blades, four fixed blades, and a discharge screen having ⅛ inch openings. The gap between the rotary and fixed blades was set to approximately 0.020 inch. The rotary knife cutter sheared the confetti-like pieces across the knife-edges, tearing the pieces apart and releasing a fibrous material at a rate of about one pound per hour. The fibrous material had a BET surface area of 0.9748 m²/g+/−0.0167 m²/g, a porosity of 89.0437 percent and a bulk density (0.53 psia) of 0.1260 g/mL. An average length of the fibers was 1.141 mm and an average width of the fibers was 0.027 mm, giving an average L/D of 42:1. A scanning electron micrograph of the fibrous material is shown in FIG. 26 at 25× magnification.

Example 2 Preparation of Fibrous Material from Bleached Kraft Board

A 1500 pound skid of virgin bleached white Kraft board having a bulk density of 30 lb/ft³ was obtained from International Paper. The material was folded flat, and then fed into a 3 hp Flinch Baugh shredder at a rate of approximately 15 to 20 pounds per hour. The shredder was equipped with two 12 inch rotary blades, two fixed blades and a 0.30 inch discharge screen. The gap between the rotary and fixed blades was adjusted to 0.10 inch. The output from the shredder resembled confetti having a width of between 0.1 inch and 0.5 inch, a length of between 0.25 inch and 1 inch and a thickness equivalent to that of the starting material (about 0.075 inch). The confetti-like material was fed to a Munson rotary knife cutter, Model SC30. The discharge screen had ⅛ inch openings. The gap between the rotary and fixed blades was set to approximately 0.020 inch. The rotary knife cutter sheared the confetti-like pieces, releasing a fibrous material at a rate of about one pound per hour. The fibrous material had a BET surface area of 1.1316 m²/g +/−0.0103 m²/g, a porosity of 88.3285 percent and a bulk density (0.53 psia) of 0.1497 g/mL. An average length of the fibers was 1.063 mm and an average width of the fibers was 0.0245 mm, giving an average L/D of 43:1. A scanning electron micrograph of the fibrous material is shown in FIG. 27 at 25× magnification.

Example 3 Preparation of Twice Sheared Fibrous Material from Bleached Kraft Board

A 1500 pound skid of virgin bleached white Kraft board having a bulk density of 301b/ft³ was obtained from International Paper. The material was folded flat, and then fed into a 3 hp Flinch Baugh shredder at a rate of approximately 15 to 20 pounds per hour. The shredder was equipped with two 12 inch rotary blades, two fixed blades and a 0.30 inch discharge screen. The gap between the rotary and fixed blades was adjusted to 0.10 inch. The output from the shredder resembled confetti (as above). The confetti-like material was fed to a Munson rotary knife cutter, Model SC30. The discharge screen had 1/16 inch openings. The gap between the rotary and fixed blades was set to approximately 0.020 inch. The rotary knife cutter the confetti-like pieces, releasing a fibrous material at a rate of about one pound per hour. The material resulting from the first shearing was fed back into the same setup described above and sheared again. The resulting fibrous material had a BET surface area of 1.4408 m²/g+/−0.0156 m²/g, a porosity of 90.8998 percent and a bulk density (@0.53 psia) of 0.1298 g/mL. An average length of the fibers was 0.891 mm and an average width of the fibers was 0.026 mm, giving an average L/D of 34:1. A scanning electron micrograph of the fibrous material is shown in FIG. 28 at 25× magnification.

Example 4 Preparation of Thrice Sheared Fibrous Material from Bleached Kraft Board

A 1500 pound skid of virgin bleached white Kraft board having a bulk density of 301b/ft³ was obtained from International Paper. The material was folded flat, and then fed into a 3 hp Flinch Baugh shredder at a rate of approximately 15 to 20 pounds per hour. The shredder was equipped with two 12 inch rotary blades, two fixed blades and a 0.30 inch discharge screen. The gap between the rotary and fixed blades was adjusted to 0.10 inch. The output from the shredder resembled confetti (as above). The confetti-like material was fed to a Munson rotary knife cutter, Model SC30. The discharge screen had ⅛ inch openings. The gap between the rotary and fixed blades was set to approximately 0.020 inch. The rotary knife cutter sheared the confetti-like pieces across the knife-edges. The material resulting from the first shearing was fed back into the same setup and the screen was replaced with a 1/16 inch screen. This material was sheared. The material resulting from the second shearing was fed back into the same setup and the screen was replaced with a 1/32 inch screen. This material was sheared. The resulting fibrous material had a BET surface area of 1.6897 m²/g+/−0.0155 m²/g, a porosity of 87.7163 percent and a bulk density (@0.53 psia) of 0.1448 g/mL. An average length of the fibers was 0.824 mm and an average width of the fibers was 0.0262 mm, giving an average L/D of 32:1. A scanning electron micrograph of the fibrous material is shown in FIG. 29 at 25× magnification.

Example 5 Preparation of Densified Fibrous Material from Bleached Kraft Board without Added Binder

Fibrous material was prepared according to Example 2. Approximately 11b of water was sprayed onto each 101b of fibrous material. The fibrous material was densified using a California Pellet Mill 1100 operating at 75° C. Pellets were obtained having a bulk density ranging from about 71b/ft³ to about 15 lb/ft³.

Example 6 Preparation of Densified Fibrous Material from Bleached Kraft Board with Binder

Fibrous material was prepared according to Example 2.

A 2 weight percent stock solution of POLYOX™ WSR N10 (polyethylene oxide) was prepared in water.

Approximately 1 lb of the stock solution was sprayed onto each 10 lb of fibrous material. The fibrous material was densified using a California Pellet Mill 1100 operating at 75° C. Pellets were obtained having a bulk density ranging from about 15 lb/ft³ to about 40 lb/ft3.

Example 7 Reducing the Molecular Weight of Cellulose in Fibrous Kraft Paper by Gamma Radiation with Minimum Oxidation

Fibrous material is prepared according to Example 4. The fibrous Kraft paper is densified according to Example 5.

The densified pellets are placed in a glass ampoule having a maximum capacity of 250 mL. The glass ampoule is evacuated under high vacuum (10⁻⁵ torr) for 30 minutes, and then back-filled with argon gas. The ampoule is sealed under argon. The pellets in the ampoule are irradiated with gamma radiation for about 3 hours at a dose rate of about 1 Mrad per hour to provide an irradiated material in which the cellulose has a lower molecular weight than the fibrous Kraft starting material.

Example 8 Reducing the Molecular Weight of Cellulose in Fibrous Kraft Paper by Gamma Radiation with Maximum Oxidation

Fibrous material is prepared according to Example 4. The fibrous Kraft paper is densified according to Example 5.

The densified pellets are placed in a glass ampoule having a maximum capacity of 250 mL. The glass ampoule is sealed under an atmosphere of air. The pellets in the ampoule are irradiated with gamma radiation for about 3 hours at a dose rate of about 1 Mrad per hour to provide an irradiated material in which the cellulose has a lower molecular weight than the fibrous Kraft starting material.

Example 9 Electron Beam Processing

Samples were treated with electron beam using a vaulted Rhodotron® TT200 continuous wave accelerator delivering 5 MeV electrons at 80 kW of output power. Table 1 describes the parameters used. Table 2 reports the nominal dose used for the Sample ID (in Mrad) and the corresponding dose delivered to the sample (in kgy).

TABLE 1 Rhodotron ® TT 200 Parameters Beam Beam Produced: Accelerated electrons Beam energy: Nominal (fixed): 10 MeV (+0 keV-250 keV Energy dispersion at 10 Mev: Full width half maximum (FWHM) 300 keV Beam power at 10 MeV: Guaranteed Operating Range 1 to 80 kW Power Consumption Stand-by condition (vacuum and cooling ON):  <15 kW At 50 kW beam power: <210 kW At 80 kW beam power: <260 kW RF System Frequency: 107.5 ± 1 MHz Tetrode type: Thomson TH781 Scanning Horn Nominal Scanning Length (measured at 25-35 120 cm cm from window): Scanning Range: From 30% to 100% of Nominal Scanning Length Nominal Scanning Frequency (at max. 100 Hz ± 5% scanning length): Scanning Uniformity (across 90% of Nominal ±5% Scanning Length)

TABLE 2 Dosages Delivered to Samples Total Dosage (Mrad) (Number Associated with Sample ID Delivered Dose (kgy)¹ 1 9.9 3 29.0 5 50.4 7 69.2 10 100.0 15 150.3 20 198.3 30 330.9 50 529.0 70 695.9 100 993.6 ¹For example, 9.9 kgy was delivered in 11 seconds at a beam current of 5 mA and a line speed of 12.9 feet/minute. Cool time between treatments was around 2 minutes.

Example 10 Methods of Determining Molecular Weight of Cellulosic and Lignocellulosic Materials by Gel Permeation Chromatography

Cellulosic and lignocellulosic materials for analysis were treated according to Example 4. Sample materials presented in the following tables include Kraft paper (P), wheat straw (WS), alfalfa (A), cellulose (C), switchgrass (SG), grasses (G), and starch (ST), and sucrose (S). The number “132” of the Sample ID refers to the particle size of the material after shearing through a 1/32 inch screen. The number after the dash refers to the dosage of radiation (MRad) and “US” refers to ultrasonic treatment. For example, a sample ID “P132-10” refers to Kraft paper that has been sheared to a particle size of 132 mesh and has been irradiated with 10 Mrad.

For samples that were irradiated with e-beam, the number following the dash refers to the amount of energy delivered to the sample. For example, a sample ID “P-100e” refers to Kraft paper that has been delivered a dose of energy of about 100 MRad or about 1000 kgy (Table 2).

TABLE 3 Peak Average Molecular Weight of Irradiated Kraft Paper Sample Dosage¹ Average MW ± Sample Source ID (Mrad) Ultrasound² Std Dev. Kraft Paper P132 0 No 32853 ± 10006 P132-10 10 ″  61398 ± 2468** P132-100 100 ″ 8444 ± 580  P132-181 181 ″ 6668 ± 77  P132-US 0 Yes 3095 ± 1013 **Low doses of radiation appear to increase the molecular weight of some materials ¹Dosage Rate = 1 MRad/hour ²Treatment for 30 minutes with 20 kHz ultrasound using a 1000 W horn under re-circulating conditions with the material dispersed in water.

TABLE 4 Peak Average Molecular Weight of Irradiated Kraft Paper with E-Beam Dosage Average MW ± Sample Source Sample ID (Mrad) Std Dev. Kraft Paper P-1e 1 63489 ± 595 P-5e 5 56587 ± 536 P-10e 10 53610 ± 327 P-30e 30 38231 ± 124 P-70e 70 12011 ± 158 P-100e 100 9770 ± 2 

TABLE 5 Peak Average Molecular Weight of Gamma Irradiated Materials Peak Dosage¹ Average MW ± Sample ID # (Mrad) Ultrasound² Std Dev. WS132 1 0 No 1407411 ± 175191 2 ″ ″ 39145 ± 3425 3 ″ ″ 2886 ± 177 WS132-10* 1 10 ″ 26040 ± 3240 WS132-100* 1 100 ″ 23620 ± 453  A132 1 0 ″ 1604886 ± 151701 2 ″ ″ 37525 ± 3751 3 ″ ″ 2853 ± 490 A132-10* 1 10 ″ 50853 ± 1665 2 ″ ″ 2461 ± 17  A132-100* 1 100 ″ 38291 ± 2235 2 ″ ″ 2487 ± 15  SG132 1 0 ″ 1557360 ± 83693  2 ″ ″ 42594 ± 4414 3 ″ ″ 3268 ± 249 SG132-10* 1 10 ″ 60888 ± 9131 SG132-100* 1 100 ″ 22345 ± 3797 SG132-10-US 1 10 Yes  86086 ± 43518 2 ″ ″ 2247 ± 468 SG132-100-US 1 100 ″  4696 ± 1465 *Peaks coalesce after treatment **Low doses of radiation appear to increase the molecular weight of some materials ¹Dosage Rate = 1 MRad/hour ²Treatment for 30 minutes with 20 kHz ultrasound using a 1000 W horn under re-circulating conditions with the material dispersed in water.

TABLE 6 Peak Average Molecular Weight of Irradiated Material with E-Beam Peak Average MW ± Sample ID # Dosage STD DEV. A-1e 1 1 1004783 ± 97518 2 34499 ± 482 3 2235 ± 1  A-5e 1 5 38245 ± 346 2 2286 ± 35 A-10e 1 10 44326 ± 33  2 2333 ± 18 A-30e 1 30 47366 ± 583 2 2377 ± 7  A-50e 1 50 32761 ± 168 2 2435 ± 6  G-1e 1 1  447362 ± 38817 2 32165 ± 779 3 3004 ± 25 G-5e 1 5  62167 ± 6418 2 2444 ± 33 G-10e 1 10  72636 ± 4075 2 3065 ± 34 G-30e 1 30 17159 ± 390 G-50e 1 50 18960 ± 142 ST 1 0 923336 ± 1883 2 150265 ± 4033 ST-1e 1 1 846081 ± 5180 2 131222 ± 1687 ST-5e 1 5  90664 ± 1370 ST-10e 1 10 98050 ± 255 ST-30e 1 30 41884 ± 223 ST-70e 1 70 9699 ± 31 ST-100e 1 100 8705 ± 38

Gel Permeation Chromatography (GPC) is used to determine the molecular weight distribution of polymers. During GPC analysis, a solution of the polymer sample is passed through a column packed with a porous gel trapping small molecules. The sample is separated based on molecular size with larger molecules eluting sooner than smaller molecules. The retention time of each component is most often detected by refractive index (RI), evaporative light scattering (ELS), or ultraviolet (UV) and compared to a calibration curve. The resulting data is then used to calculate the molecular weight distribution for the sample.

A distribution of molecular weights rather than a unique molecular weight is used to characterize synthetic polymers. To characterize this distribution, statistical averages are utilized. The most common of these averages are the “number average molecular weight” (M_(n)) and the “weight average molecular weight” (M_(w)).

M_(n) is similar to the standard arithmetic mean associated with a group of numbers. When applied to polymers, M_(n) refers to the average molecular weight of the molecules in the polymer. M_(n) is calculated affording the same amount of significance to each molecule regardless of its individual molecular weight. The average M, is calculated by the following formula where N_(i) is the number of molecules with a molar mass equal to M_(i).

${\overset{\_}{M}}_{n} = \frac{\sum\limits_{i}\; {N_{i}M_{i}}}{\sum\limits_{i}\; N_{i}}$

M_(w) is another statistical descriptor of the molecular weight distribution that places a greater emphasis on larger molecules than smaller molecules in the distribution. The formula below shows the statistical calculation of the weight average molecular weight.

${\overset{\_}{M}}_{w} = \frac{\sum\limits_{i}\; {N_{i}M_{i}^{2}}}{\sum\limits_{i}\; {N_{i}M_{i}}}$

The polydispersity index or PI is defined as the ratio of M_(w)/M_(n). The larger the PI, the broader or more disperse the distribution. The lowest value that a PI can be is 1. This represents a monodisperse sample; that is, a polymer with all of the molecules in the distribution being the same molecular weight.

The peak molecular weight value (M_(P)) is another descriptor defined as the mode of the molecular weight distribution. It signifies the molecular weight that is most abundant in the distribution. This value also gives insight to the molecular weight distribution.

Most GPC measurements are made relative to a different polymer standard. The accuracy of the results depends on how closely the characteristics of the polymer being analyzed match those of the standard used. The expected error in reproducibility between different series of determinations, calibrated separately, is ca. 5-10% and is characteristic to the limited precision of GPC determinations. Therefore, GPC results are most useful when a comparison between the molecular weight distributions of different samples is made during the same series of determinations.

The lignocellulosic samples required sample preparation prior to GPC analysis. First, a saturated solution (8.4% by weight) of lithium chloride (LiCl) was prepared in dimethyl acetamide (DMAc). Approximately 100 mg of the sample was added to approximately 10 g of a freshly prepared saturated LiCl/DMAc solution, and the mixture was heated to approximately 150° C.-170° C. with stirring for 1 hour. The resulting solutions were generally light- to dark-yellow in color. The temperature of the solutions were decreased to approximately 100° C. and heated for an additional 2 hours. The temperatures of the solutions were then decreased to approximately 50° C. and the sample solution was heated for approximately 48 to 60 hours. Of note, samples irradiated at 100 MRad were more easily solubilized as compared to their untreated counterpart. Additionally, the sheared samples (denoted by the number 132) had slightly lower average molecular weights as compared with uncut samples.

The resulting sample solutions were diluted 1:1 using DMAc as solvent and were filtered through a 0.45 μm PTFE filter. The filtered sample solutions were then analyzed by GPC using the parameters described in Table 7. The peak average molecular weights (Mp) of the samples, as determined by Gel Permeation Chromatography (GPC), are summarized in Tables 3-6. Each sample was prepared in duplicate and each preparation of the sample was analyzed in duplicate (two injections) for a total of four injections per sample. The EasiCal® polystyrene standards PS1A and PS1B were used to generate a calibration curve for the molecular weight scale from about 580 to 7,500,00 Daltons.

TABLE 7 GPC Analysis Conditions Instrument: Waters Alliance GPC 2000 Columns (3): Plgel 10μ Mixed-B S/N's: 10M-MB-148-83; 10M-MB- 148-84; 10M-MB-174-129 Mobile Phase (solvent): 0.5% LiCl in DMAc (1.0 mL/min.) Column/Detector Temperature: 70° C. Injector Temperature: 70° C. Sample Loop Size: 323.5 μL

Example 11 Time-Of-Flight Secondary Ion Mass Spectrometry (ToF-SIMS) Surface Analysis

Time-of-Flight Secondary Ion Mass Spectroscopy (ToF-SIMS) is a surface-sensitive spectroscopy that uses a pulsed ion beam (Cs or microfocused Ga) to remove molecules from the very outermost surface of the sample. The particles are removed from atomic monolayers on the surface (secondary ions). These particles are then accelerated into a “flight tube” and their mass is determined by measuring the exact time at which they reach the detector (i.e. time-of-flight). ToF-SIMS provides detailed elemental and molecular information about the surface, thin layers, interfaces of the sample, and gives a full three-dimensional analysis. The use is widespread, including semiconductors, polymers, paint, coatings, glass, paper, metals, ceramics, biomaterials, pharmaceuticals and organic tissue. Since ToF-SIMS is a survey technique, all the elements in the periodic table, including H, are detected. ToF-SIMS data is presented in Tables 8-11. Parameters used are reported in Table 12.

TABLE 8 Normalized Mean Intensities of Various Positive Ions of Interest (Normalized relative to total ion counts × 10000) P132 P132-10 P132-100 m/z species Mean σ Mean σ Mean σ 23 Na 257 28 276 54 193 36 27 Al 647 43 821 399 297 44 28 Si 76 45.9 197 89 81.7 10.7 15 CH₃ 77.9 7.8 161 26 133 12 27 C₂H₃ 448 28 720 65 718 82 39 C₃H₃ 333 10 463 37 474 26 41 C₃H₅ 703 19 820 127 900 63 43 C₃H₇ 657 11 757 162 924 118 115 C₉H₇ 73 13.4 40.3 4.5 42.5 15.7 128 C₁₀H₈ 55.5 11.6 26.8 4.8 27.7 6.9 73 C₃H₉Si* 181 77 65.1 18.4 81.7 7.5 147 C₅H₁₅OSi₂* 72.2 33.1 24.9 10.9 38.5 4 207 C₅H₁₅O₃Si₃* 17.2 7.8 6.26 3.05 7.49 1.77 647 C₄₂H₆₄PO₃ 3.63 1.05 1.43 1.41 10.7 7.2

TABLE 9 Normalized Mean Intensities of Various Negative Ions of Interest (Normalized relative to total ion counts × 10000) P132 P132-10 P132-100 m/z species Mean σ Mean σ Mean σ 19 F 15.3 2.1 42.4 37.8 19.2 1.9 35 Cl 63.8 2.8 107 33 74.1 5.5 13 CH 1900 91 1970 26 1500 6 25 C₂H 247 127 220 99 540 7 26 CN 18.1 2.1 48.6 30.8 43.9 1.4 42 CNO 1.16 0.71 0.743 0.711 10.8 0.9 46 NO₂ 1.87 0.38 1.66 1.65 12.8 1.8

TABLE 10 Normalized Mean Intensities of Various Positive Ions of Interest (Normalized relative to total ion counts × 10000) P-1e P-5e P-10e P-30e P-70e P-100e m/z species Mean σ Mean σ Mean σ Mean σ Mean σ Mean σ 23 Na 232 56 370 37 241 44 518 57 350 27 542 104 27 Al 549 194 677 86 752 371 761 158 516 159 622 166 28 Si 87.3 11.3 134 24 159 100 158 32 93.7 17.1 124 11 15 CH₃ 114 23 92.9 3.9 128 18 110 16 147 16 141 5 27 C₂H₃ 501 205 551 59 645 165 597 152 707 94 600 55 39 C₃H₃ 375 80 288 8 379 82 321 57 435 61 417 32 41 C₃H₅ 716 123 610 24 727 182 607 93 799 112 707 84 43 C₃H₇ 717 121 628 52 653 172 660 89 861 113 743 73 115 C₉H₇ 49.9 14.6 43.8 2.6 42.2 7.9 41.4 10.1 27.7 8 32.4 10.5 128 C₁₀H₈ 38.8 13.1 39.2 1.9 35.2 11.8 31.9 7.8 21.2 6.1 24.2 6.8 73 C₃H₉Si* 92.5 3.0 80.6 2.9 72.3 7.7 75.3 11.4 63 3.4 55.8 2.1 147 C₅H₁₅OSi₂* 27.2 3.9 17.3 1.2 20.4 4.3 16.1 1.9 21.7 3.1 16.3 1.7 207 C₅H₁₅O₃Si₃* 6.05 0.74 3.71 0.18 4.51 0.55 3.54 0.37 5.31 0.59 4.08 0.28 647 C₄₂H₆₄PO₃ 1.61 1.65 1.09 1.30 0.325 0.307 nd ~ 0.868 1.31 0.306 0.334

TABLE 11 Normalized Mean Intensities of Various Negative Ions of Interest (Normalized relative to total ion counts × 10000) P-1e P-5e P-10e P-30e P-70e P-100e m/z species Mean σ Mean σ Mean σ Mean σ Mean σ Mean σ 13 CH 1950 72 1700 65 1870 91 1880 35 2000 46 2120 102 25 C₂H 154 47 98.8 36.3 157 4 230 17 239 22 224 19 19 F 25.4 1 24.3 1.4 74.3 18.6 40.6 14.9 25.6 1.9 21.5 2 35 Cl 39.2 13.5 38.7 3.5 46.7 5.4 67.6 6.2 45.1 2.9 32.9 10.2 26 CN 71.9 18.9 6.23 2.61 28.1 10.1 34.2 29.2 57.3 28.9 112 60 42 CNO 0.572 0.183 0.313 0.077 0.62 0.199 1.29 0.2 1.37 0.55 1.38 0.28 46 NO₂ 0.331 0.057 0.596 0.255 0.668 0.149 1.44 0.19 1.92 0.29 0.549 0.1

TABLE 12 ToF-SIMS Parameters Instrument Conditions: Instrument: PHI TRIFT II Primary Ion Source: ⁶⁹Ga Primary Ion Beam Potential: 12 kV + ions 18 kV − ions Primary Ion Current (DC): 2 na for P#E samples 600 pA for P132 samples Energy Filter/CD: Out/Out Masses Blanked: None Charge Compensation: On

ToF-SIMS uses a focused, pulsed particle beam (typically Cs or Ga) to dislodge chemical species on a materials surface. Particles produced closer to the site of impact tend to be dissociated ions (positive or negative). Secondary particles generated farther from the impact site tend to be molecular compounds, typically fragments of much larger organic macromolecules. The particles are then accelerated into a flight path on their way towards a detector. Because it is possible to measure the “time-of-flight” of the particles from the time of impact to detector on a scale of nano-seconds, it is possible to produce a mass resolution as fine as 0.00X atomic mass units (i.e. one part in a thousand of the mass of a proton). Under typical operating conditions, the results of ToF-SIMS analysis include: a mass spectrum that surveys all atomic masses over a range of 0-10,000 amu, the rastered beam produces maps of any mass of interest on a sub-micron scale, and depth profiles are produced by removal of surface layers by sputtering under the ion beam. Negative ion analysis showed that the polymer had increasing amounts of CNO, CN, and NO₂ groups.

Example 12 X-Ray Photoelectron Spectroscopy (XPS)/Electron Spectroscopy for Chemical Analysis (ESCA)

X-Ray Photoelectron Spectroscopy (XPS) (sometimes called “ESCA”) measures the chemical composition of the top five nanometers of surface; XPS uses photo-ionization energy and energy-dispersive analysis of the emitted photoelectrons to study the composition and electronic state of the surface region of a sample. X-ray Photoelectron spectroscopy is based upon a single photon in/electron out. Soft x-rays stimulate the ejection of photoelectrons whose kinetic energy is measured by an electrostatic electron energy analyzer. Small changes to the energy are caused by chemically-shifted valence states of the atoms from which the electrons are ejected; thus, the measurement provides chemical information about the sample surface.

TABLE 13 Atomic Concentrations (in %)^(a, b) Atom Sample ID C O Al Si P132 (Area1) 57.3 39.8 1.5 1.5 P132 (Area2) 57.1 39.8 1.6 1.5 P132-10 (Area 1) 63.2 33.5 1.7 1.6 P132-10 (Area 2) 65.6 31.1 1.7 1.7 P132-100 (Area 1) 61.2 36.7 0.9 1.2 P132-100 (Area 2) 61 36.9 0.8 1.3 ^(a) Normalized to 100% of the elements detected. XPS does not detect H or He.

TABLE 14 Carbon Chemical State (in % C) Sample ID C—C, C—H C—O C═O O—C═O P132 (Area1) 22 49 21 7 P132 (Area2) 25 49 20 6 P132-10 (Area 1) 34 42 15 9 P132-10 (Area 2) 43 38 14 5 P132-100 (Area 1) 27 45 15 9 P132-100 (Area 2) 25 44 23 9

TABLE 15 Atomic Concentrations (in %)^(a,b) Atom Sample ID C O Al Si Na P-1e (Area 1) 59.8 37.9 1.4 0.9 ~ P-1e (Area 2) 58.5 38.7 1.5 1.3 ~ P-5e (Area 1) 58.1 39.7 1.4 0.8 ~ P-5e (Area 2) 58.0 39.7 1.5 0.8 ~ P-10e (Area 1) 61.6 36.7 1.1 0.7 ~ P-10e (Area 2) 58.8 38.6 1.5 1.1 ~ P-50e (Area 1) 59.9 37.9 1.4 0.8 <0.1 P-50e (Area 2) 59.4 38.3 1.4 0.9 <0.1 P-70e (Area 1) 61.3 36.9 1.2 0.6 <0.1 P-70e (Area 2) 61.2 36.8 1.4 0.7 <0.1 P-100e (Area 1) 61.1 37.0 1.2 0.7 <0.1 P-100e (Area 2) 60.5 37.2 1.4 0.9 <0.1 ^(a)Normalized to 100% of the elements detected. XPS does not detect H or He. ^(b)A less than symbol “<” indicates accurate quantification cannot be made due to weak signal intensity.

TABLE 16 Carbon Chemical State Table (in % C) Sample ID C—C, C—H C—O C═O O—C═O P-1e (Area 1) 29 46 20 5 P-1e (Area 2) 27 49 19 5 P-5e (Area 1) 25 53 18 5 P-5e (Area 2) 28 52 17 4 P-10e (Area 1) 33 47 16 5 P-10e (Area 2) 28 51 16 5 P-50e (Area 1) 29 45 20 6 P-50e (Area 2) 28 50 16 5 P-70e (Area 1) 32 45 16 6 P-70e (Area 2) 35 43 16 6 P-100e (Area 1) 32 42 19 7 P-100e (Area 2) 30 47 16 7

TABLE 17 Analytical Parameters Instrument: PHI Quantum 2000 X-ray source: Monochromated Alk_(α) 1486.6 eV Acceptance Angle: ±23° Take-off angle: 45° Analysis area: 1400 × 300 μm Charge Correction: C1s 284.8 eV

XPS spectra are obtained by irradiating a material with a beam of aluminum or magnesium X-rays while simultaneously measuring the kinetic energy (KE) and number of electrons that escape from the top 1 to 10 nm of the material being analyzed (see analytical parameters, Table 17). The XPS technique is highly surface specific due to the short range of the photoelectrons that are excited from the solid. The energy of the photoelectrons leaving the sample is determined using a Concentric Hemispherical Analyzer (CHA) and this gives a spectrum with a series of photoelectron peaks. The binding energy of the peaks is characteristic of each element. The peak areas can be used (with appropriate sensitivity factors) to determine the composition of the materials surface. The shape of each peak and the binding energy can be slightly altered by the chemical state of the emitting atom. Hence XPS can provide chemical bonding information as well. XPS is not sensitive to hydrogen or helium, but can detect all other elements. XPS requires ultra-high vacuum (UHV) conditions and is commonly used for the surface analysis of polymers, coatings, catalysts, composites, fibers, ceramics, pharmaceutical/medical materials, and materials of biological origin. XPS data is reported in Tables 13-16.

Example 13 Raman Analysis

Raman spectra were acquired from the surface of fibers from samples: P132, P 132-100, P-1e, and P-100e. The measurements were performed using a “LabRam” J-Y Spectrometer. A HeNe laser (632.8 nm wavelength) and 600 gr/mm grating were used for the measurements. The measurements were performed confocally using backscattering geometry (180°) under an Olympus BX40 microscope. The samples had a Raman spectrum typical of cellulose.

Example 14 Scanning Probe Microscopy (SPM) Surface Analysis Using an Atomic Force Microscope (AFM)

The purpose of this analysis was to obtain Atomic Force Microscope (AFM) images of the samples in Tables 18 and 19 to measure surface roughness.

Scanning probe microscopy (SPM) is a branch of microscopy that forms images of surfaces using a physical probe that scans the specimen. An image of the surface is obtained by mechanically moving the probe in a raster scan of the specimen, line by line, and recording the probe-surface interaction as a function of position. The atomic force microscope (AFM) or scanning force microscope (SFM) is a very high-resolution type of scanning probe microscope, with demonstrated resolution of fractions of a nanometer, more than 1000 times better than the optical diffraction limit. The probe (or the sample under a stationary probe) generally is moved by a piezoelectric tube. Such scanners are designed to be moved precisely in any of the three perpendicular axes (x,y,z). By following a raster pattern, the sensor data forms an image of the probe-surface interaction. Feedback from the sensor is used to maintain the probe at a constant force or distance from the object surface. For atomic force microscopy, the sensor is a position-sensitive photodetector that records the angle of reflection from a laser bean focused on the top of the cantilever.

TABLE 18 Roughness Results for Gamma-Irradiated Samples Sample ID RMS (Å) R_(a) (Å) R_(max) (Å) P132 927.2 716.3 8347.6 P132-10 825.7 576.8 11500 P132-100 1008 813.5 7250.7

TABLE 19 Roughness Results for Samples Irradiated with E-Beam Sample ID RMS (Å) R_(a) (Å) R_(max) (Å) P-1e 1441.2 1147.1 8955.4 P-5e 917.3 727.5 6753.4 P-10e 805.6 612.1 7906.5 P-30e 919.2 733.7 6900 P-70e 505.8 388.1 5974.2 P-100e 458.2 367.9 3196.9

AFM images were collected using a NanoScope III Dimension 5000 (Digital Instruments, Santa Barbara, Calif., USA). The instrument was calibrated against a NIST traceable standard with an accuracy better than 2%. NanoProbe silicon tips were used. Image processing procedures involving auto-flattening, plane fitting or convolution were employed.

One 5 μm×5 μm area was imaged at a random location on top of a single fiber. Perspective (3-D) views of these surfaces are included with vertical exaggerations noted on the plots (FIGS. 29A-29F). The roughness analyses were performed and are expressed in: (1) Root-Mean-Square Roughness, RMS; (2) Mean Roughness, R^(a); and (3) Maximum Height (Peak-to-Valley), Rmax. Results are summarized in Tables 18 and 19.

Example 15 Determining Crystallinity of Irradiated Materials by X-Ray Diffraction

X-ray diffraction (XRD) is a method by which a crystalline sample is irradiated with monoenergetic x-rays. The interaction of the lattice structure of the sample with these x-rays is recorded and provides information about the crystalline structure being irradiated. The resulting characteristic “fingerprint” allows for the identification of the crystalline compounds present in the sample. Using a whole-pattern fitting analysis (the Rietvelt Refinement), it is possible to perform quantitative analyses on samples containing more than one crystalline compound.

TABLE 20 XRD Data Including Domain Size and % Crystallinity Domain Size Sample ID (Å) % Crystallinity P132 55 55 P132-10 46 58 P132-100 50 55 P132-181 48 52 P132-US 26 40 A132 28 42 A132-10 26 40 A132-100 28 35 WS132 30 36 WS132-10 27 37 WS132-100 30 41 SG132 29 40 SG132-10 28 38 SG132-100 28 37 SG132-10-US 25 42 SG132-100-US 21 34

Each sample was placed on a zero background holder and placed in a Phillips PW1800 diffractometer using Cu radiation. Scans were then run over the range of 5° to 50° with a step size of 0.05° and a counting time of 2 hours each.

Once the diffraction patterns were obtained, the phases were identified with the aid of the Powder Diffraction File published by the International Centre for Diffraction Data. In all samples the crystalline phase identified was cellulose—Ia, which has a triclinic structure.

The distinguishing feature among the 20 samples is the peak breadth, which is related to the crystallite domain size. The experimental peak breadth was used to compute the domain size and percent crystallinity, which are reported in Table 4.

Percent crystallinity (X_(c)%) is measured as a ratio of the crystalline area to the total area under the x-ray diffraction peaks,

${X_{c\;}\%} = {\frac{A_{C}}{\left\{ {A_{a} + A_{C}} \right\}} \times 100\%}$

where,

-   -   A_(c)=Area of crystalline phase     -   A_(a)=Area of amorphous phase     -   X_(c)=Percent of crystallinity

To determine the percent crystallinity for each sample it was necessary to first extract the amount of the amorphous phase. This is done by estimating the area of each diffraction pattern that can be attributed to the crystalline phase (represented by the sharper peaks) and the non-crystalline phase (represented by the broad humps beneath the pattern and centered at 22° and 38°).

A systematic process was used to minimize error in these calculations due to broad crystalline peaks as well as high background intensity. First, a linear background was applied and then removed. Second, two Gaussian peaks centered at 22° and 38° with widths of 10-12° each were fitted to the humps beneath the crystalline peaks. Third, the area beneath the two broad Gaussian peaks and the rest of the pattern were determined. Finally, percent crystallinity was calculated by dividing the area beneath the crystalline peak by the total intensity (after background subtraction). Domain size and % crystallinity of the samples as determined by X-ray diffraction (XRD) are presented in Table 20.

Example 16 Porosimetry Analysis of Irradiated Materials

Mercury pore size and pore volume analysis (Table 21) is based on forcing mercury (a non-wetting liquid) into a porous structure under tightly controlled pressures. Since mercury does not wet most substances and will not spontaneously penetrate pores by capillary action, it must be forced into the voids of the sample by applying external pressure. The pressure required to fill the voids is inversely proportional to the size of the pores. Only a small amount of force or pressure is required to fill large voids, whereas much greater pressure is required to fill voids of very small pores.

TABLE 21 Pore Size and Volume Distribution by Mercury Porosimetry Median Median Average Bulk Total Total Pore Pore Pore Density Apparent Intrusion Pore Diameter Diameter Diameter @ 0.50 (skeletal) Volume Area (Volume) (Area) (4V/A) psia Density Porosity Sample ID (mL/g) (m²/g) (μm) (μm) (μm) (g/mL) (g/mL) (%) P132 6.0594 1.228 36.2250 13.7278 19.7415 0.1448 1.1785 87.7163 P132-10 5.5436 1.211 46.3463 4.5646 18.3106 0.1614 1.5355 89.4875 P132-100 5.3985 0.998 34.5235 18.2005 21.6422 0.1612 1.2413 87.0151 P132-181 3.2866 0.868 25.3448 12.2410 15.1509 0.2497 1.3916 82.0577 P132-US 6.0005 14.787 98.3459 0.0055 1.6231 0.1404 0.8894 84.2199 A132 2.0037 11.759 64.6308 0.0113 0.6816 0.3683 1.4058 73.7990 A132-10 1.9514 10.326 53.2706 0.0105 0.7560 0.3768 1.4231 73.5241 A132-100 1.9394 10.205 43.8966 0.0118 0.7602 0.3760 1.3889 72.9264 SG132 2.5267 8.265 57.6958 0.0141 1.2229 0.3119 1.4708 78.7961 SG132-10 2.1414 8.643 26.4666 0.0103 0.9910 0.3457 1.3315 74.0340 SG132-100 2.5142 10.766 32.7118 0.0098 0.9342 0.3077 1.3590 77.3593 SG132-10-US 4.4043 1.722 71.5734 1.1016 10.2319 0.1930 1.2883 85.0169 SG132-100-US 4.9665 7.358 24.8462 0.0089 2.6998 0.1695 1.0731 84.2010 WS132 2.9920 5.447 76.3675 0.0516 2.1971 0.2773 1.6279 82.9664 WS132-10 3.1138 2.901 57.4727 0.3630 4.2940 0.2763 1.9808 86.0484 WS132-100 3.2077 3.114 52.3284 0.2876 4.1199 0.2599 1.5611 83.3538 A-1e 1.9535 3.698 25.3411 0.0810 2.1130 0.3896 1.6299 76.0992 A-5e 1.9697 6.503 29.5954 0.0336 1.2117 0.3748 1.4317 73.8225 A-10e 2.0897 12.030 45.5493 0.0101 0.6948 0.3587 1.4321 74.9545 A-50e 2.1141 7.291 37.0760 0.0304 1.1599 0.3577 1.4677 75.6264 G-1e 2.4382 7.582 58.5521 0.0201 1.2863 0.3144 1.3472 76.6610 G-5e 2.4268 6.436 44.4848 0.0225 1.5082 0.3172 1.3782 76.9831 G-10e 2.6708 6.865 62.8605 0.0404 1.5562 0.2960 1.4140 79.0638 G-50e 2.8197 6.798 56.5048 0.0315 1.6591 0.2794 1.3179 78.7959 P-1e 7.7692 1.052 49.8844 22.9315 29.5348 0.1188 1.5443 92.3065 P-5e 7.1261 1.212 46.6400 12.3252 23.5166 0.1268 1.3160 90.3644 P-10e 6.6096 1.113 41.4252 17.4375 23.7513 0.1374 1.4906 90.7850 P-50e 6.5911 1.156 40.7837 15.9823 22.7974 0.1362 1.3302 89.7616 P-100e 5.3507 1.195 35.3622 10.7400 17.9063 0.1648 1.3948 88.1840 S 0.4362 0.030 102.8411 42.5047 57.8208 0.9334 1.5745 40.7160 S-1e 0.3900 0.632 90.6808 0.0041 2.4680 0.9772 1.5790 38.1140 S-5e 0.3914 0.337 97.1991 0.0070 4.6406 0.9858 1.6052 38.5847 S-10e 0.4179 0.349 113.4360 0.0042 4.7873 0.9469 1.5669 39.5678 S-30e 0.4616 5.329 102.0559 0.0042 0.3464 0.9065 1.5585 41.8388 S-50e 0.5217 7.162 137.2124 0.0051 0.2914 0.8521 1.5342 44.4582 S-100e 0.8817 15.217 76.4577 0.0053 0.2318 0.6478 1.5105 57.1131 St 0.6593 17.631 4.2402 0.0053 0.1496 0.7757 1.5877 51.1438 St-1e 0.6720 18.078 4.3360 0.0052 0.1487 0.7651 1.5750 51.4206 St-5e 0.6334 19.495 4.2848 0.0051 0.1300 0.7794 1.5395 49.3706 St-10e 0.6208 16.980 4.3362 0.0056 0.1462 0.7952 1.5703 49.3630 St-30e 0.6892 18.066 4.4152 0.0050 0.1526 0.7475 1.5417 51.5165 St-50e 0.6662 18.338 4.3759 0.0054 0.1453 0.7637 1.5548 50.8778 St-100e 0.6471 23.154 5.4032 0.0048 0.1118 0.7229 1.3582 46.7761

The AutoPore 9520 can attain a maximum pressure of 414 MPa or 60,000 psia. There are four low pressure stations for sample preparation and collection of macropore data from 0.2 psia to 50 psia. There are two high pressure chambers, which collect data from 25 psia to 60,000 psia. The sample is placed in a bowl-like apparatus called a penetrometer, which is bonded to a glass capillary stem with a metal coating. As mercury invades the voids in and around the sample, it moves down the capillary stem. The loss of mercury from the capillary stem results in a change in the electrical capacitance. The change in capacitance during the experiment is converted to volume of mercury by knowing the stem volume of the penetrometer in use. A variety of penetrometers with different bowl (sample) sizes and capillaries are available to accommodate most sample sizes and configurations. Table 22 below defines some of the key parameters calculated for each sample.

TABLE 22 Definition of Parameters Parameter Description Total Intrusion Volume: The total volume of mercury intruded during an experiment. This can include interstitial filling between small particles, porosity of sample, and compression volume of sample. Total Pore Area: The total intrusion volume converted to an area assuming cylindrical shaped pores. Median Pore Diameter The size at the 50^(th) percentile on the cumulative volume graph. (volume): Median Pore Diameter (area): The size at the 50^(th) percentile on the cumulative area graph. Average Pore Diameter: The total pore volume divided by the total pore area (4V/A). Bulk Density: The mass of the sample divided by the bulk volume. Bulk volume is determined at the filling pressure, typically 0.5 psia. Apparent Density: The mass of sample divided by the volume of sample measured at highest pressure, typically 60,000 psia. Porosity: (Bulk Density/Apparent Density) × 100%

Example 17 Particle Size Analysis of Irradiated Materials

The technique of particle sizing by static light scattering is based on Mie theory (which also encompasses Fraunhofer theory). Mie theory predicts the intensity vs. angle relationship as a function of the size for spherical scattering particles provided that other system variables are known and held constant. These variables are the wavelength of incident light and the relative refractive index of the sample material. Application of Mie theory provides the detailed particle size information. Table 23 summarizes particle size using median diameter, mean diameter, and modal diameter as parameters.

TABLE 23 Particle Size by Laser Light Scattering (Dry Sample Dispersion) Median Mean Diameter Modal Diameter Sample ID Diameter (μm) (μm) (μm) A132 380.695 418.778 442.258 A132-10 321.742 366.231 410.156 A132-100 301.786 348.633 444.169 SG132 369.400 411.790 455.508 SG132-10 278.793 325.497 426.717 SG132-100 242.757 298.686 390.097 WS132 407.335 445.618 467.978 WS132-10 194.237 226.604 297.941 WS132-100 201.975 236.037 307.304

Particle size was determined by Laser Light Scattering (Dry Sample Dispersion) using a Malvern Mastersizer 2000 using the following conditions:

Feed Rate: 35% Disperser Pressure: 4 Bar Optical Model: (2.610, 1.000i), 1.000

An appropriate amount of sample was introduced onto a vibratory tray. The feed rate and air pressure were adjusted to ensure that the particles were properly dispersed. The key component is selecting an air pressure that will break up agglomerations, but does not compromise the sample integrity. The amount of sample needed varies depending on the size of the particles. In general, samples with fine particles require less material than samples with coarse particles.

Example 18 Surface Area Analysis of Irradiated Materials

Surface area of each sample was analyzed using a Micromeritics ASAP 2420 Accelerated Surface Area and Porosimetry System. The samples were prepared by first degassing for 16 hours at 40° C. Next, free space (both warm and cold) with helium is calculated and then the sample tube is evacuated again to remove the helium. Data collection begins after this second evacuation and consists of defining target pressures, which control how much gas is dosed onto the sample. At each target pressure, the quantity of gas adsorbed and the actual pressure are determined and recorded. The pressure inside the sample tube is measured with a pressure transducer. Additional doses of gas will continue until the target pressure is achieved and allowed to equilibrate. The quantity of gas adsorbed is determined by summing multiple doses onto the sample. The pressure and quantity define a gas adsorption isotherm and are used to calculate a number of parameters, including BET surface area (Table 24).

TABLE 24 Summary of Surface Area by Gas Adsorption BET Surface Sample ID Single point surface area (m²/g) Area (m²/g) P132 @ P/Po = 0.250387771 1.5253 1.6897 P132-10 @ P/Po = 0.239496722 1.0212 1.2782 P132-100 @ P/Po = 0.240538100 1.0338 1.2622 P132-181 @ P/Po = 0.239166091 0.5102 0.6448 P132-US @ P/Po = 0.217359072 1.0983 1.6793 A132 @ P/Po = 0.240040610 0.5400 0.7614 A132-10 @ P/Po = 0.211218936 0.5383 0.7212 A132-100 @ P/Po = 0.238791097 0.4258 0.5538 SG132 @ P/Po = 0.237989353 0.6359 0.8350 SG132-10 @ P/Po = 0.238576905 0.6794 0.8689 SG132-100 @ P/Po = 0.241960361 0.5518 0.7034 SG132-10-US @ P/Po = 0.225692889 0.5693 0.7510 SG132-100-US @ P/Po = 0.225935246 1.0983 1.4963 G-10-US 0.751 G100-US 1.496 G132-US 1.679 WS132 @ P/Po = 0.237823664 0.6582 0.8663 WS132-10 @ P/Po = 0.238612476 0.6191 0.7912 WS132-100 @ P/Po = 0.238398832 0.6255 0.8143 A-1e @ P/Po = 0.238098138 0.6518 0.8368 A-5e @ P/Po = 0.243184477 0.6263 0.7865 A-10e @ P/Po = 0.243163236 0.4899 0.6170 A-50e @ P/Po = 0.243225512 0.4489 0.5730 G-1e @ P/Po = 0.238496102 0.5489 0.7038 G-5e @ P/Po = 0.242792602 0.5621 0.7086 G-10e @ P/Po = 0.243066031 0.5021 0.6363 G-50e @ P/Po = 0.238291132 0.4913 0.6333 P-1e @ P/Po = 0.240842223 1.1413 1.4442 P-5e @ P/Po = 0.240789274 1.0187 1.3288 P-10e @ P/Po = 0.240116967 1.1015 1.3657 P-50e @ P/Po = 0.240072114 1.0089 1.2593 P-100e @ P/Po = 0.236541386 0.9116 1.1677 S @ P/Po = 0.225335038 0.0147 0.0279 S-1e @ P/Po = 0.217142291 0.0193 0.0372 S-5e @ P/Po = 0.133107838 0.0201 0.0485 S-10e @ P/Po = 0.244886517 0.0236 0.0317 S-30e @ P/Po = 0.237929400 0.0309 0.0428 S-50e @ P/Po = 0.245494494 0.0262 0.0365 S-100e @ P/Po = 0.224698551 0.0368 0.0506 St @ P/Po = 0.238324949 0.3126 0.4013 St-1e @ P/Po = 0.238432726 0.3254 0.4223 St-5e @ P/Po = 0.238363587 0.3106 0.4071 St-10e @ P/Po = 0.238341099 0.3205 0.4268 St-30e @ P/Po = 0.238629889 0.3118 0.4189 St-50e @ P/Po = 0.244630980 0.3119 0.3969 St-100e @ P/Po = 0.238421621 0.2932 0.3677

The BET model for isotherms is a widely used theory for calculating the specific surface area. The analysis involves determining the monolayer capacity of the sample surface by calculating the amount required to cover the entire surface with a single densely packed layer of krypton. The monolayer capacity is multiplied by the cross sectional area of a molecule of probe gas to determine the total surface area. Specific surface area is the surface area of the sample aliquot divided by the mass of the sample.

Example 19 Fiber Length Determination of Irradiated Materials

Fiber length distribution testing was performed in triplicate on the samples submitted using the Techpap MorFi LB01 system. The average fiber length and width are reported in Table 25.

TABLE 25 Summary of Lignocellulosic Fiber Length and Width Data Statistically Corrected Average Average Arithmetic Length Length Width Average Weighted in Weighted in (micrometers) Sample ID (mm) Length (mm) Length (mm) (μm) P132-10 0.484 0.615 0.773 24.7 P132-100 0.369 0.423 0.496 23.8 P132-181 0.312 0.342 0.392 24.4 A132-10 0.382 0.423 0.650 43.2 A132-100 0.362 0.435 0.592 29.9 SG132-10 0.328 0.363 0.521 44.0 SG132-100 0.325 0.351 0.466 43.8 WS132-10 0.353 0.381 0.565 44.7 WS132-100 0.354 0.371 0.536 45.4

Example 20 Ultrasonic Treatment of Irradiated and Un-irradiated Switchgrass

Switchgrass was sheared according to Example 4. The switchgrass was treated by ultrasound alone or irradiation with 10 Mrad or 100 Mrad of gamma rays, and then sonicated. The resulting materials correspond to G132-BR (un-irradiated), G132-10-BR (10 Mrad and sonication) and G132-100-BR (100 Mrad and sonication), as presented in Table 1. Sonication was performed on each sample for 30 minutes using 20 kHz ultrasound from a 1000W horn under re-circulating conditions. Each sample was dispersed in water at a concentration of about 0.10 g/mL.

FIGS. 30 and 31 show the apparatus used for sonication. Apparatus 500 includes a converter 502 connected to booster 504 communicating with a horn 506 fabricated from titanium or an alloy of titanium. The horn, which has a seal 510 made from VITON® about its perimeter on its processing side, forms a liquid tight seal with a processing cell 508. The processing side of the horn is immersed in a liquid, such as water, that has dispersed therein the sample to be sonicated. Pressure in the cell is monitored with a pressure gauge 512. In operation, each sample is moved by pump 517 from tank 516 through the processing cell and is sonicated. After, sonication, the sample is captured in tank 520. The process can be reversed in that the contents of tank 520 can be sent through the processing cell and captured in tank 516. This process can be repeated a number of times until a desired level of processing is delivered to the sample.

Example 21 Scanning Electron Micrographs of Un-irradiated Switchgrass in Comparison to Irradiated and Irradiated and Sonicated Switchgrass

Switchgrass samples for the scanning electron micrographs were applied to carbon tape and gold sputter coated (70 seconds). Images were taken with a JEOL 6500 field emission scanning electron microscope.

FIG. 32 is a scanning electron micrograph at 1000× magnification of a fibrous material produced from shearing switchgrass on a rotary knife cutter, and then passing the sheared material through a 1/32 inch screen.

FIGS. 33 and 34 are scanning electron micrographs of the fibrous material of FIG. 32 after irradiation with 10 Mrad and 100 Mrad gamma rays, respectively, at 1000× magnification.

FIG. 35 is a scanning electron micrographs of the fibrous material of FIG. 32 after irradiation with 10 Mrad and sonication at 1000× magnification.

FIG. 36 is a scanning electron micrographs of the fibrous material of FIG. 32 after irradiation with 100 Mrad and sonication at 1000× magnification.

Example 22 Fourier Transform Infrared (FT-IR) Spectrum of Irradiated and Unirradiated Kraft Paper

FT-IR analysis was performed on a Nicolet/Impact 400. The results indicate that samples P132, P132-10, P132-100, P-1e, P-5e, P-10e, P-30e, P-70e, and P-100e are consistent with a cellulose-based material.

FIG. 37 is an infrared spectrum of Kraft board paper sheared according to Example 4, while FIG. 38 is an infrared spectrum of the Kraft paper of FIG. 37 after irradiation with 100 Mrad of gamma radiation. The irradiated sample shows an additional peak in region A (centered about 1730 cm⁻¹) that is not found in the un-irradiated material. Of note, an increase in the amount of a carbonyl absorption at 1650 cm⁻¹ was detected when going from P132 to P132-10 to P132-100. Similar results were observed for the samples P-1e, P-5e, P-10e, P-30e, P-70e, and P-100e.

Example 23 Proton and Carbon-13 Nuclear Magnetic Resonance (¹H-NMR and ¹³C-NMR)

Spectra of Irradiated and Unirradiated Kraft Paper

Sample Preparation

The samples P132, P132-10, P132-100, P-1e, P-5e, P-10e, P-30e, P-70e, and P-100e were prepared for analysis by dissolution with DMSO-d₆ with 2% tetrabutyl ammonium fluoride trihydrate. The samples that had undergone lower levels of irradiation were significantly less soluble than the samples with higher irradiation. Unirradiated samples formed a gel in this solvent mixture, but heating to 60° C. resolved the peaks in the NMR spectra. The samples having undergone higher levels of irradiation were soluble at a concentration of 10% wt/wt.

Analysis

¹H-NMR spectra of the samples at 15 mg/mL showed a distinct very broad resonance peak centered at 16 ppm (FIGS. 38A-38J). This peak is characteristic of an exchangeable —OH proton for an enol and was confirmed by a “d₂O shake.” Model compounds (acetylacetone, glucuronic acid, and keto-gulonic acid) were analyzed and made a convincing case that this peak was indeed an exchangeable enol proton. This proposed enol peak was very sensitive to concentration effects, and we were unable to conclude whether this resonance was due to an enol or possibly a carboxylic acid.

The carboxylic acid proton resonances of the model compounds were similar to what was observed for the treated cellulose samples. These model compounds were shifted up field to 5-6 ppm. Preparation of P-100e at higher concentrations (˜10% wt/wt) led to the dramatic down field shifting to where the carboxylic acid resonances of the model compounds were found (˜6 ppm) (FIG. 38N). These results lead to the conclusion that this resonance is unreliable for characterizing this functional group, however the data suggests that the number of exchangeable hydrogens increases with increasing irradiation of the sample. Also, no vinyl protons were detected.

The ¹³C NMR spectra of the samples confirm the presence of a carbonyl of a carboxylic acid or a carboxylic acid derivative. This new peak (at 168 ppm) is not present in the untreated samples (FIG. 38K). A ¹³C NMR spectrum with a long delay allowed the quantitation of the signal for P-100e (FIGS. 38L-38M). Comparison of the integration of the carbonyl resonance to the resonances at approximately 100 ppm (the C1 signals) suggests that the ratio of the carbonyl carbon to C1 is 1:13.8 or roughly 1 carbonyl for every 14 glucose units. The chemical shift at 100 ppm correlates well with glucuronic acid.

Titration

Samples P-100e and P132-100 (1 g) were suspended in deionized water (25 mL). The indicator alizarin yellow was added to each sample with stirring. P-100e was more difficult to wet. Both samples were titrated with a solution of 0.2M NaOH. The end point was very subtle and was confirmed by using pH paper. The starting pH of the samples was ˜4 for both samples. P132-100 required 0.4 milliequivalents of hydroxide, which gives a molecular weight for the carboxylic acid of 2500 amu. If 180 amu is used for a monomer, this suggests there is one carboxylic acid group for 13.9 monomer units. Likewise, P-100e required 3.2 milliequivalents of hydroxide, which calculates to be one carboxylic acid group for every 17.4 monomer units.

Conclusions

The C-6 carbon of cellulose appears to be oxidized to the carboxylic acid (a glucuronic acid derivative) in this oxidation is surprisingly specific. This oxidation is in agreement with the IR band that grows with irradiation at ˜1740 cm⁻¹, which corresponds to an aliphatic carboxylic acid. The titration results are in agreement with the quantitative ¹³C NMR. The increased solubility of the sample with the higher levels of irradiation correlates well with the increasing number of carboxylic acid protons. A proposed mechanism for the degradation of “C-6 oxidized cellulose” is provided below in Scheme 1.

Example 24 Combination of Electron Beam and Sonication Pretreatment

Switchgrass is used as the feedstock and is sheared with a Munson rotary knife cutter into a fibrous material. The fibrous material is then evenly distributed onto an open tray composed of tin with an area of greater than about 500 in2. The fibrous material is distributed so that it has a depth of about 1-2 inches in the open tray. The fibrous material may be distributed in plastic bags at lower doses of irradiation (under 10 MRad), and left uncovered on the metal tray at higher doses of radiation.

Separate samples of the fibrous material are then exposed to successive doses of electron beam radiation to achieve a total dose of 1 Mrad, 2 Mrad, 3, Mrad, 5 Mrad, 10 Mrad, 50 Mrad, and 100 Mrad. Some samples are maintained under the same conditions as the remaining samples, but are not irradiated, to serve as controls. After cooling, the irradiated fibrous material is sent on for further processing through a sonication device.

The sonication device includes a converter connected to booster communicating with a horn fabricated from titanium or an alloy of titanium. The horn, which has a seal made from VITON® about its perimeter on its processing side, forms a liquid tight seal with a processing cell. The processing side of the horn is immersed in a liquid, such as water, into which the irradiated fibrous material to be sonicated is immersed. Pressure in the cell is monitored with a pressure gauge. In operation, each sample is moved by pump through the processing cell and is sonicated.

To prepare the irradiated fibrous material for sonication, the irradiated fibrous material is removed from any container (e.g., plastic bags) and is dispersed in water at a concentration of about 0.10 g/mL. Sonication is performed on each sample for 30 minutes using 20 kHz ultrasound from a 1000 W horn under re-circulating conditions. After sonication, the irradiated fibrous material is captured in a tank. This process can be repeated a number of times until a desired level of processing is achieved based on monitoring the structural changes in the switchgrass. Again, some irradiated samples are kept under the same conditions as the remaining samples, but are not sonicated, to serve as controls. In addition, some samples that were not irradiated are sonicated, again to serve as controls. Thus, some controls are not processed, some are only irradiated, and some are only sonicated.

Example 25 Microbial Testing of Pretreated Biomass

Specific lignocellulosic materials pretreated as described herein are analyzed for toxicity to common strains of yeast and bacteria used in the biofuels industry for the fermentation step in ethanol production. Additionally, sugar content and compatibility with cellulase enzymes are examined to determine the viability of the treatment process. Testing of the pretreated materials is carried out in two phases as follows.

Phase 1:Toxicity and Sugar Content

Toxicity of the pretreated grasses and paper feedstocks is measured in yeast Saccharomyces cerevisiae (wine yeast) and Pichia stipitis (ATCC 66278) as well as the bacteria Zymomonas mobilis (ATCC 31821) and Clostridium thermocellum (ATCC 31924). A growth study is performed with each of the organisms to determine the optimal time of incubation and sampling.

Each of the feedstocks is then incubated, in duplicate, with S. cerevisiae, P. stipitis, Z. mobilis, and C. thermocellum in a standard microbiological medium for each organism. YM broth is used for the two yeast strains, S. cerevisiae and P. stipitis. RM medium is used for Z. mobilis and CM4 medium for C. thermocellum. A positive control, with pure sugar added, but no feedstock, is used for comparison. During the incubation, a total of five samples is taken over a 12 hour period at time 0, 3, 6, 9, and 12 hours and analyzed for viability (plate counts for Z. mobilis and direct counts for S. cerevisiae) and ethanol concentration.

Sugar content of the feedstocks is measured using High Performance Liquid Chromatography (HPLC) equipped with either a Shodex™ sugar SP0810 or Biorad Aminex® HPX-87P column. Each of the feedstocks (approx. 5 g) is mixed with reverse osmosis (RO) water for 1 hour. The liquid portion of the mixture is removed and analyzed for glucose, galactose, xylose, mannose, arabinose, and cellobiose content. The analysis is performed according to National Bioenergy Center protocol Determination of Structural Carbohydrates and Lignin in Biomass.

Phase 2: Cellulase Compatibility

Feedstocks are tested, in duplicate, with commercially available Accellerase™ 1000, which contains a complex of enzymes that reduces lignocellulosic biomass into fermentable sugars, at the recommended temperature and concentration in an Erlenmeyer flask. The flasks are incubated with moderate shaking at around 200 rpm for 12 hours. During that time, samples are taken every three hours at time 0, 3, 6, 9, and 12 hours to determine the concentration of reducing sugars (Hope and Dean, Biotech J., 1974, 144:403) in the liquid portion of the flasks.

Example 26 Sugar Concentration Analysis using HPLC

13 samples were analyzed for sugar concentration (HPLC) and toxicity against 3 microorganisms (Pichia stipitis, Saccharomyces cerevisiae, and Zymomonas mobilis. Table 26 lists the equipment used for these experiments. Table 27 and 28 provide a list of the sugars (including vendor and lot numbers) used to prepare the HPLC standard and the protocol used to prepare the HPLC standard, respectively.

TABLE 26 Equipment Utilized in Experiments Equipment Manufacturer, Name pH meter Orion Shakers (2) B. Braun Biotech, Certomat BS-1 HPLC Waters, 2690 HPLC Module Spectrophotometer Unicam, UV300 YSI Biochem Analyzer Interscience, YSI

TABLE 27 Sugars used in HPLC analysis Sugar Manufacturer Ref # Lot # glucose BioChemika 49140 1284892 xylose 95731 1304473 51707231 cellobiose 22150 1303157 14806191 arabinose 10840 1188979 24105272 mannose 63582 363063/1 22097 galactose 48259 46032/1 33197

TABLE 28 Preparation of HPLC standards Desired Volume of Total Concentration Volume of sugar Nanopure Water Volume (mg/mL) solution (mL) (mL) 4   50 mL of 4 mg/mL 0 50 2   25 mL of 4 mg/mL 25 50 1   25 mL of 2 mg/mL 25 50 0.5   25 mL of 1 mg/mL 25 50 0.1    5 ml of 1 mg/mL 20 25 Verification 18.75 mL of 4 mg/mL 31.25 50 Standard 1.5 mg/mL

Analysis

Each sample (1 gram) was mixed with reverse osmosis water at 200 rpm and 50° C. overnight. The pH of the sample was adjusted to between 5 and 6 and filtered through a 0.2 μm syringe filter. Samples were stored at −20° C. prior to analysis to maintain integrity of the samples. The observations made during the preparation of the samples are presented in Table 29.

TABLE 29 Observations During HPLC Sample Preparation Amount Water used added Sample (g) (mL) pH Observations P132 1 30 5.38 Fluffy, difficult to mix P132-10 1 25 6.77 Fluffy, difficult to mix P132-100 1 20 3.19 pH is low, difficult to bring to pH 5.0, used 10 N NaOH P132-US 0.3 5 6.14 A132 1 15 5.52 A132-10 1 15 4.9 A132-100 1 15 5.39 SG132 1 15 5.59 SG132-10 1 15 5.16 SG132-100 1 15 4.7 SG132-10-US 0.3 5 5.12 SG132-100-US 0.3 5 4.97 WS132 1 15 5.63 WS132-10 1 15 5.43 WS132-100 1 15 5.02 *pH of these samples was adjusted to pH using 1N NaOH

Standards were prepared fresh from a 4 mg/mL stock solution of the 6 combined sugars, glucose, xylose, cellobiose, arabinose, mannose, and galactose. The stock solution was prepared by dissolving 0.400 grams of each sugar into 75 mL of nanopure water (0.3 micron filtered). Once dissolved, the stock solution was diluted to 100 mL using a volumetric flask and stored at −20° C. Working standard solutions of 0.1, 0.5, 1, 2, and 4 mg/mL were prepared by serial dilution of the stock solution with nanopure water. In addition, a verification standard of 1.5 mg/mL was also prepared from the stock solution.

Sugar concentrations were analyzed according to the protocol Determination of Structural Carbohydrates in Biomass (NREL Biomass Program, 2006) and this protocol is incorporated herein by reference in its entirety. A SHODEX SUGAR SP0810 COLUMN with an Evaporative Light Scattering Detector was used. A verification standard (1.5 mg/mL of standard) was analyzed every 8 injections to ensure that the integrity of the column and detector were maintained during the experiment. The standard curve coefficient of variation (R² value) was at least 0.989 and the concentration of the verification standards were within 10% of the actual concentration. The HPLC conditions were as follows:

TABLE 30 HPLC Parameters Injection volume: 20 μL Mobile phase: nanopure water*, 0.45 μm filtered and degassed Flow rate: 0.5 mL/min Column 85° C. temperature: Detector evaporator temperature temperature: 110° C., nebulizer temperature 90° C. *Initial tests noted that better separation was observed when using nanopure water than 15/85 acetonitrile:water in the mobile phase (manufacturer does not recommend using greater than 20% acetonitrile with this column).

Results

The results of the HPLC analysis are presented in Tables 31, 32, and 33.

TABLE 31 Sugar Concentration Expressed as mg/mL and mg/g of Extract Xylose Arabinose Glucose Cellobiose mW ~150 mW ~150 mW ~180 Galactose Mannose mW ~342 C₅H₁₀O₅ C₅H₁₀O₅ C₆H₁₂O₆ (see gluc) (see gluc) C₁₂H₂₂O₁₁ Mono Mono Mono mg/mL:mg/g mg/mL:mg/g Disacc Sample ID mg/mL mg/g mg/mL mg/g mg/mL mg/g mg/mL mg/g mg/mL mg/g mg/mL mg/g P P-132 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 0.00 P-132-10 0.00 0.00 0.00 0.00 0.34 8.60 0.00 0.00 0.00 0.00 00.33 8.13 P-132-100 0.35 7.04 0.00 0.00 0.34 6.14 0.00 0.00 0.00 0.00 0.36 7.20 P-132-BR 0.35 5.80 0.43 7.17 0.34 5.62 0.00 0.00 0.00 0.00 0.00 0.00 G G-132 0.39 5.88 0.38 5.73 0.84 12.66 0.34 5.04 0.92 13.76 0.00 0.00 G-132-10 0.50 7.50 0.41 6.18 1.07 16.04 0.35 5.19 0.98 14.66 0.00 0.00 G-132-100 0.00 0.00 0.37 5.54 0.41 6.14 0.00 0.00 0.55 8.28 0.45 6.71 G-132-10-US 0.34 5.73 0.39 6.45 0.33 5.43 0.00 0.00 0.00 0.00 0.00 0.00 G-132-100-US 0.00 0.00 0.37 6.22 0.35 5.90 0.33 5.43 0.40 6.70 0.39 6.45 A A-132 1.36 20.39 0.00 0.00 1.08 16.22 0.39 5.84 1.07 16.02 0.00 0.00 A-132-10 1.19 17.87 0.00 0.00 0.00 0.00 0.00 0.00 0.37 5.52 0.00 0.00 A-132-100 1.07 16.11 0.00 0.00 0.35 5.18 0.00 0.00 0.00 0.00 0.81 12.2 WS WS-132 0.49 7.41 0.41 6.15 0.39 5.90 0.00 0.00 0.00 0.00 0.00 0.00 WS-132-10 0.57 8.49 0.40 5.99 0.73 10.95 0.34 5.07 0.50 7.55 0.00 0.00 WS-132-100 0.43 6.39 0.37 5.51 0.36 5.36 0.00 0.00 0.36 5.33 0.35 5.25

TABLE 32 Sugar Concentration Expressed at % of Paper Sugar concentration (% of dry sample) P132 P132-10 P132-100 P132-US cellobiose 0.00 0.81 0.72 0.00 glucose 0.00 0.86 0.67 0.56 xylose 0.00 0.00 0.70 0.58 galactose 0.00 0.00 0.00 0.00 arabinose 0.00 0.00 0.00 0.72 mannose 0.00 0.00 0.00 0.00

TABLE 33 Sugar Concentration Expressed at % of Total Sample Sugar concentration (% of dry A132- A132- SG132- SG132- SG132- SG132- WS132- WS132- sample) A132 10 100 SG132 10 100 10-US 100-US WS132 10 100 cellobiose 0.00 0.00 1.22 0.00 0.00 0.67 0.00 0.65 0.00 0.00 0.53 glucose 1.62 0.00 0.52 1.27 1.60 0.61 0.54 0.59 0.59 1.10 0.54 xylose 2.04 1.79 1.61 0.59 0.75 0.00 0.57 0.00 0.74 0.85 0.64 galactose 0.58 0.00 0.00 0.50 0.52 0.00 0.00 0.54 0.00 0.51 0.00 arabinose 0.00 0.00 0.00 0.57 0.62 0.55 0.65 0.62 0.62 0.60 0.55 mannose 1.60 0.55 0.00 1.38 1.47 0.83 0.00 0.67 0.00 0.76 0.53

Example 27 Toxicity Study

Twelve samples were analyzed for toxicity against a panel of three ethanol-producing cultures. In this study, glucose was added to the samples in order to distinguish between starvation of the cultures and toxicity of the samples. A thirteenth sample was tested for toxicity against Pichia stipitis. A summary of the protocol used is listed in Table 32. A description of the chemicals and equipment used in the toxicity testing is reported in Tables 34-36.

TABLE 34 Conditions for Toxicity Testing Organism Saccharomyces Pichia Zymomonas cerevesiae stipitis mobilis ATCC NRRL Variable ATCC 31821 24858 Y-7124 Test Repetition Duplicate Inoculation Volume (mL) 1 0.1 1 Incubation Temperature 30° C. 25° C. 25° C. Shaker Speed (rpm) 125 200 125 Erlenmeyer Flask Volume 250 mL 500 mL 250 mL Media volume 100 mL 100 mL 100 mL Total Incubation time 36 36 48 (hours) Ethanol Analysis 24, 30, 36 24, 30, 36 24, 36, 48 (hours) Cell Counts (hours) 24, 36 24, 36 24, 48 pH 0 hours 0 hours 0 hours

TABLE 35 Reagents Used for Toxicity Testing Media Component Manufacturer Reference # Lot # Urea SchoIAR Chemistry 9472706 AD-7284-43 Yeast Nitrogen Becton Dickinson 291940 7128171 Base Peptone Becton Dickinson 211677 4303198 Xylose Fluka 95731 1304473 51707231 Glucose Sigma G-5400 107H0245 Yeast Extract Becton Dickinson 288620 4026828 (used for S. cerevisiae) Yeast Extract Becton Dickinson 212750 7165593 (used for P. stipitis and Z. mobilis) MgSO₄•7H₂O Sigma M5921 034K0066 (NH₄)₂SO₄ Sigma A4418 117K5421 KH₂PO₄ Sigma P5379 074K0160 YM Broth Becton Dickinson 271120 6278265

TABLE 36 YSI Components Used in Shake Flask Study Component Catalog # Lot # YSI Ethanol Membrane 2786 07L100153 YSI Ethanol Standard (3.2 g/L) 2790 012711040 YSI Ethanol Buffer 2787 07M1000053, 07100215

Testing was performed using the three microorganisms as described below. Saccharomyces cerevisiae ATCC 24858 (American Type Culture Collection) A slant of S. cerevisiae was prepared from a rehydrated lyophilized culture obtained from ATCC. A portion of the slant material was streaked onto an YM Broth+20 g/L agar (pH 5.0) and incubated at 30° C. for 2 days. A 250 mL Erlenmeyer flask containing 50 mL of medium (20 g/L glucose, 3 g/L yeast extract, and 5.0 g/L peptone, pH 5.0) was inoculated with one colony from the YM plate and incubated for 24 hours at 25° C. and 200 rpm. After 23 hours of growth, a sample was taken and analyzed for optical density (600 nm in a UV spectrophotometer) and purity (Gram stain). Based on these results, one flask (called the Seed Flask) with an OD of 14.8 and clean Gram Stain was chosen to inoculate all of the test flasks.

The test vessels were 500 mL Erlenmeyer flasks containing 100 mL of the sterile medium described above. All flasks were autoclaved at 121° C. and 15 psi prior to the addition of the test materials. The test materials were not sterilized, as autoclaving will change the content of the samples. The test samples were added at the time of inoculation (rather than prior to) to reduce the possibility of contamination. In addition to the test samples, 1 mL (1% v/v) of seed flask material was added to each flask. The flasks were incubated as described above for 36 hours.

Pichia stipitis NRRL Y-7124 (ARS Culture Collection)

A slant of P. stipitis was prepared from a rehydrated lyophilized culture obtained from ARS Culture Collection. A portion of the slant material was streaked onto an YM Broth+20 g/L agar (pH 5.0) and incubated at 30° C. for 2 days. A 250 mL Erlenmeyer flask containing 100 mL of medium (40 g/L glucose, 1.7 g/L yeast nitrogen base, 2.27 g/L urea, 6.56 g/L peptone, 40 g/L xylose, pH 5.0) was inoculated with a small amount of plate material and incubated for 24 hours at 25° C. and 125 rpm. After 23 hours of growth, a sample was taken and analyzed for optical density (600 nm in a UV spectrophotometer) and purity (Gram stain). Based on these results, one flask (called the Seed Flask) at an optical density of 5.23 and with a clean Gram Stain was chosen to inoculate all of the test flasks.

The test vessels were 250 mL Erlenmeyer flasks containing 100 mL of the sterile medium described above. All flasks were autoclaved empty at 121° C. and 15 psi and filter sterilized (0.22 μm filter) media added to the flasks prior to the addition of the test materials. The test materials were not sterilized, as autoclaving will change the content of the samples and filter sterilization not appropriate for sterilization of solids. The test samples were added at the time of inoculation (rather than prior to) to reduce the possibility of contamination. In addition to the test samples, 1 mL (1% v/v) of seed flask material was added to each flask. The flasks were incubated as described above for 48 hours.

Zymomonas mobilis ATCC 31821 (American Type Culture)

A slant of Z. mobilis was prepared from a rehydrated lyophilized culture obtained from ATTC. A portion of the slant material was streaked onto DYE plates (glucose 20 g/L, Yeast Extract 10 g/L, Agar 20 g/L, pH 5.4) and incubated at 30° C. and 5% CO₂ for 2 days. A 20 mL screw-cap test tube containing 15 mL of medium (25 g/L glucose, 10 g/L yeast extract, 1 g/L MgSO₄.7H₂O, 1 g/L (NH₄)₂SO₄, 2 g/L KH₂PO₄, pH 5.4) was inoculated with one colony and incubated for 24 hours at 30° C. with no shaking. After 23 hours of growth, a sample was taken and analyzed for optical density (600 nm in a UV spectrophotometer) and purity (gram stain). Based on these results, one tube (OD 1.96) was chosen to inoculate the second seed flask. The second seed flask was a 125 ml flask containing 70 mL of the media described above and was inoculated with 700 μL (1% v/v) and incubated for 24 hours at 30° C. with no shaking. After 23 hours of growth, a sample was taken and analyzed for optical density (600 nm in a UV spectrophotometer) and purity (gram stain). Based on these results, one flask (called the Seed Flask) with an OD of 3.72 was chosen to inoculate all of the test flasks.

The test vessels were 250 mL Erlenmeyer flasks containing 100 mL of the sterile medium described above with the exception of yeast extract at 5 g/L. All flasks were autoclaved empty at 121° C. and 15 psi and filter sterilized (0.22 μm filter) media added to the flasks prior to the addition of the test materials. The test materials were not sterilized, as autoclaving will change the content of the samples and filter sterilization not appropriate for sterilization of solids. The test samples were added at the time of inoculation to reduce the possibility of contamination. In addition to the test samples, 1 mL (1% v/v) of seed flask material was added to each flask. The flasks were incubated as described above for 36 hours

Analysis

Two samples were analyzed for cell concentration (using spread plating for Z. mobilis and direct counts (haemocytometer and microscope for S. cerevisiae and P. stipitis). Appropriately diluted samples of Z. mobilis were spread on Dextrose Yeast Extract (glucose 20 g/L, Yeast Extract 10 g/L, Agar 20 g/L, pH 5.4) plates, incubated at 30° C. and 5% CO₂ for 2 days, and the number of colonies counted. Appropriately diluted samples of S. cerevisiae and P. stipitis were mixed with 0.05% Trypan blue, loaded into a Neubauer haemocytometer. The cells were counted under 40× magnification.

Three samples were analyzed for ethanol concentration using the YSI Biochem Analyzer based on the alcohol dehydrogenase assay (YSI, Interscience). Samples were centrifuged at 14,000 rpm for 20 minutes and the supernatant stored at −20° C. to preserve integrity. The samples were diluted to between 0-3.2 g/L ethanol prior to analysis. A standard of 3.2 g/L ethanol was analyzed approximately every 30 samples to ensure the integrity of the membrane was maintained during analysis. The optical density (600 nm) of the samples is not reported because the solid test samples interfered with absorbance measurement by increasing the turbidity of the samples and are inaccurate.

Results of Ethanol Analysis

Performance was used to compare each sample to the control for each microorganism (Tables 37-39). However, the % performance cannot be used to compare between strains. When comparing strains, the total concentration of ethanol should be used. When analyzing the data, a % performance of less than 80% may indicate toxicity when accompanied by low cell number. The equation used to determine % performance is:

% Performance=(ethanol in the sample/ethanol in control)×100

TABLE 37 Ethanol Concentration and % Performance Using Saccharomyces cerevisiae 24 hours 30 hours 36 hours Ethanol Ethanol Ethanol Concentration % Concentration % Concentration % Sample # (g/L) Performance (g/L) Performance (g/L) Performance P132 4.0 140 5.2 127 3.26 176 P132-10 4.2 147 5.1 125 3.86 209 P132-100 4.3 149 5.6 136 3.47 187 A132 5.5 191 6.5 160 5.24 283 A132-10 1.9 67 6.3 153 5.54 299 A132-100 4.4 154 5.6 137 4.04 218 G132 5.3 186 6.0 146 3.99 215 G132-10 5.2 180 6.4 156 4.63 250 G132-100 5.5 191 6.3 155 4.60 248 WS132 4.8 168 6.3 155 4.51 244 WS132-10 4.9 172 6.0 146 4.55 246 WS132-100 4.9 170 5.7 140 4.71 254 Control 2.9 100 4.1 100 1.85 100

TABLE 38 Ethanol Concentration and % Performance Using Pichia stipitis 24 hours 36 hours 48 hours Ethanol Ethanol Ethanol Concentration % Concentration % Concentration % Sample # (g/L) Performance (g/L) Performance (g/L) Performance P132 2.8 130 3.4 188 8.1 176 P132-10 7.3 344 11.9 655 15.8 342 P132-100 5.2 247 8.6 472 13.3 288 A132 12.2 575 14.7 812 14.9 324 A132-10 15.1 710 18.7 1033 26.0 565 A132-100 10.9 514 16.7 923 22.2 483 G132 8.0 375 12.9 713 13.3 288 G132-10 10.1 476 16.0 884 22.3 485 G132-100 8.6 406 15.2 837 21.6 470 WS132 9.8 460 14.9 820 17.9 389 WS132-10 7.8 370 16.1 890 19.3 418 WS132-100 9.1 429 15.0 829 15.1 328 Sample A* 13.2 156 19.0 166 20.6 160 Control 2.1 100 1.8 100 4.6 100 Samples in BOLD were the highest ethanol producers, over 20 g/L and similar to the concentrations in wood hydrolyzates (H.K. Sreenath and T.W. Jeffries Bioresource Technology 72 (2000) 253-260). *Analyzed in later shake flask experiment.

TABLE 39 Ethanol Concentration and % Performance Using Zymomonas mobilis 24 hours 30 hours 36 hours Ethanol Ethanol Ethanol Concentration Concentration Concentration % Sample # (g/L) % Performance (g/L) % Performance (g/L) Performance P132 7.5 85 6.8 84 7.5 93 P132-10 7.5 85 4.8 59 6.8 84 P132-100 7.3 83 6.2 77 7.1 88 A132 9.6 109 8.3 103 9.1 112 A132-10 9.2 105 8.4 105 8.8 109 A132-100 8.2 93 7.6 94 7.6 93 WS132 7.9 89 7.1 88 7.7 94 WS132-10 8.2 93 6.8 85 7.3 90 WS132-100 8.7 98 6.9 86 8.3 102 G132 8.7 99 7.1 88 8.1 99 G132-10 7.8 88 7.0 88 7.3 90 G132-100 8.6 98 7.8 98 8.3 102 Control 8.8 100 8.0 100 8.1 100 Results from Cell Concentration Analysis

% Cells is used to compare each sample to the control for each organism (Tables 40-42). However, the % cells cannot be used to compare between strains. When comparing strains, the total concentration of cells should be used. When analyzing the data, a % performance of less than 70% may indicate toxicity when accompanied by low ethanol concentration. The equation used to determine % performance is:

% cells=(number of cell in the sample/number of cells in control)×100

TABLE 40 Results from Cell Concentration Analysis for Saccharomyces cerevisiae 24 hours 36 hours Cell Cell Concentration Concentration Sample # (×10⁸/mL) % Cells (×10⁸/mL) % Cells P132 1.99 166 2.51 83 P132-10 2.51 209 1.91 63 P132-100 1.35 113 1.99 66 A132 3.80 316 2.59 85 A132-10 1.73 144 3.90 129 A132-100 3.98 331 2.51 83 G132 2.14 178 3.12 103 G132-10 2.33 194 2.59 85 G132-100 3.57 298 2.66 88 WS132 4.10 341 2.66 88 WS132-10 2.63 219 2.81 93 WS132-100 2.29 191 2.40 79 Control 1.20 100 3.03 100

TABLE 41 Results from Cell Concentration Analysis for Pichia stipitis 24 hours 48 hours Cell Cell Concentration Concentration Sample # (×10⁸/mL) % Cells (×10⁸/mL) % Cells P132 16.4 108 20.3 87 P132-10 11.5 76 9.5 41 P132-100 6.5 43 17.8 76 A132 7.1 47 10.2 44 A132-10 12.7 84 9.3 40 A132-100 11.8 78 18.3 78 G132 4.5 30 4.8 21 G132-10 22.8 151 9.8 42 G132-100 10.1 67 21.7 93 WS132 17.6 117 8.2 35 WS132-10 5.3 35 10.8 46 WS132-100 9.3 62 10.7 46 Control 15.1 100 23.4 100

TABLE 42 Results from Cell Concentration Analysis for Zymomonas mobilis 24 hours 36 hours Cell Cell Concentration Concentration Sample # (×10⁸/mL) % Cells (×10⁸/mL) % Cells P132 7.08 86 2.97 66 P132-10 21.80 264 4.37 98 P132-100 4.50 54 3.35 75 A132 6.95 84 1.99 44 A132-10 6.13 74 4.05 91 A132-100 9.60 116 4.20 94 G132 7.48 90 3.84 86 G132-10 14.75 178 2.89 65 G132-100 6.00 72 2.55 57 WS132 9.70 117 4.55 102 WS132-10 13.20 160 4.32 97 WS132-100 5.15 62 2.89 65 Control 8.27 100 4.47 100

Example 28 Shake Flask Fermentation of Cellulose Samples Using P. stipitis Summary

Thirteen samples were tested for ethanol production in P. stipitis culture without sugar added. They were tested in the presence and absence of cellulase (Accellerase 1000® enzyme complex, Genencor). Equipment and reagents used for the experiment are listed below in Tables 43-45.

TABLE 43 Equipment and frequency of maintenance Equipment Manufacturer Frequency of Maintenance Shakers (2) B. Braun Biotech, Quarterly Certomat BS-1 Spectrophotometer Unicam, UV300 Biannual YSI Biochem Analyzer Interscience, YSI Monthly

TABLE 44 YSI Components used in shake flask study Component Catalog # Lot# YSI Ethanol Membrane 2786 07L100153 YSI Ethanol Standard (3.2 2790 012711040 g/L) YSI Ethanol Buffer 2787 07M1000053, 07100215

TABLE 45 Chemicals used for shake flask fermentation Media Component Manufacturer Reference # Lot # Urea ScholAR 9472706 AD-7284-43 Chemistry Yeast Nitrogen Becton Dickinson 291940 7128171 Base Peptone Becton Dickinson 211677 4303198 YM Broth Becton Dickinson 271120 6278265 Accellerase ® Genencor Accellerase ® 1600794133 Enzyme complex 1000 Xylose BioChemika 95731 1304473 51707231 Glucose Sigma G-5400 107H0245

A slant of P. stipitis NRRL Y-7124 was prepared from a rehydrated lyophilized culture obtained from ARS Culture Collection. A portion of the slant material was streaked onto a Yeast Mold (YM) Broth+20 g/L agar (pH 5.0) and incubated at 30° C. for 2 days. A 250 mL Erlenmeyer flask containing 100 mL of medium (40 g/L glucose, 1.7 g/L yeast nitrogen base, 2.27 g/L urea, 6.56 g/L peptone, 40 g/L xylose, pH 5.0) was inoculated with one colony and incubated for 24 hours at 25° C. and 100 rpm. After 23 hours of growth, a sample was taken and analyzed for optical density (600 nm in a UV spectrophotometer) and purity (Gram stain). Based on these results, one flask (called the Seed Flask) at an optical density of 6.79 and with a clean Gram stain was chosen to inoculate all of the test flasks.

The test vessels were 250 mL Erlenmeyer flasks containing 100 mL of medium (1.7 g/L yeast nitrogen base, 2.27 g/L urea, and 6.56 g/L peptone). No sugar (glucose or xylose) was added to the growth flask medium. All flasks were autoclaved empty at 121° C. and 15 psi and filter sterilized (0.22 μm filter) media added to the flasks prior to the addition of the test materials. The test materials were not sterilized, as autoclaving will change the content of the samples and filter sterilization is not appropriate for sterilization of solids. The test samples (listed in Table 46) were added at the time of inoculation (rather than prior to) to reduce the possibility of contamination. In addition to the test samples, 1 mL (1% v/v) of seed flask material was added to each flask. Flasks containing sample P132-100 required the addition of 0.4 mL 1 M NaOH to bring the pH to 5.0. The flasks were incubated at 30° C. and 150 rpm above for 96 hours.

One set of duplicate flasks per feedstock contained Accellerase® enzyme complex (1.25 mL per flask, highest recommended dosage is 0.25 mL per gram of biomass, Genencor) to attempt simultaneous saccharification and fermentation (SSF). The other set of duplicate flasks did not contain Accellerase® enzyme complex. A total of 52 flasks were analyzed.

Six control flasks were also analyzed. Positive control flasks contained SolkaFloc 200 NF Powdered Cellulose (lot # UA158072, International Fiber Corporation) at a concentration of 2.5 grams per 100 mL flask (25 grams per L) with and without addition of Accellerase® enzyme complex. In addition, a control containing sugars (glucose and xylose) only was used.

TABLE 46 The amount of each feedstock added to each flask Amount added to Flask Xyleco Number (g/100 mL) P132 2.5 P132-10 2.5 P132-100 2.5 A132 5 A132-10 5 A132-100 5 G132 5 G132-10 5 G132-100 5 WS132 5 WS132-10 5 WS132-100 5 Sample A 5

Analysis

Samples were analyzed for ethanol concentration (Tables 47, 48, and 49) using the YSI Biochem Analyzer based on the alcohol dehydrogenase assay (YSI, Interscience). Samples were centrifuged at 14,000 rpm for 20 minutes and the supernatant stored at −20° C. The samples were diluted to between 0-3.2 g/L ethanol prior to analysis. A standard of 2.0 g/L ethanol was analyzed approximately every 30 samples to ensure the integrity of the membrane was maintained during analysis.

Results

TABLE 47 Results of Control Flasks Ethanol Concentration (g/L) Control 24 hours 36 hours 48 hours 96 hours Containing Glucose, no 13.20 19.00 20.60 21.60 cellulose, no enzyme Containing Crystalline 0.00 0.00 0.00 0.00 Cellulose (Solka Floc), no sugar, no enzyme Containing Crystalline 6.56 7.88 9.80 8.65 Cellulose (Solka Floc) at 25 g/L, no sugar, Accellerase ® added

TABLE 48 Results of Shake Flasks without Accellerase ® 1000 Enzyme Complex Ethanol Concentration (g/L) Sample Number 24 hours 36 hours 48 hours 96 hours P132 0.09 0.00 0.00 0.12 P132-10 0.02 0.01 0.02 0.17 P132-100 0.09 0.01 0.00 0.02 A132 1.74 1.94 2.59 3.70 A132-10 1.82 2.36 2.30 2.96 A132-100 0.30 0.73 1.31 2.38 G132 0.40 0.09 0.24 0.42 G132-10 0.69 0.42 0.22 0.24 G132-100 0.19 0.05 0.05 0.21 WS132 0.47 0.50 0.68 0.65 WS132-10 0.47 0.49 0.34 0.92 WS132-100 0.14 0.07 0.08 0.22 Sample A 1.88 1.89 2.30 3.28

TABLE 49 Results of Shake Flasks with Accellerase ® 1000 Enzyme Complex Ethanol Concentration (g/L) Sample Number 24 hours 36 hours 48 hours 96 hours P132 7.04 8.72 9.30 5.80 P132-10 4.22 4.48 4.49 1.24 P132-100 3.18 4.28 4.70 3.35 A132 2.79 2.91 2.03 4.30 A132-10 3.31 1.62 2.11 2.71 A132-100 2.06 1.92 1.02 1.47 G132 0.87 0.40 0.32 0.44 G132-10 1.38 1.04 0.63 0.07 G132-100 2.21 2.56 2.34 0.12 WS132 1.59 1.47 1.07 0.99 WS132-10 1.92 1.18 0.73 0.23 WS132-100 2.90 3.69 3.39 0.27 Sample A 2.21 2.35 3.39 2.98

Example 29 Cellulase Assay Summary

Thirteen samples were tested for cellulase susceptibility using an industry cellulase (Accellerase® 1000, Genencor) under optimum conditions of temperature and pH.

Protocol

The protocol is a modification of the NREL “Laboratory Analytical Procedure LAP-009 Enzymatic Saccharification of Lignocellulosic Biomass”. A sample of material was added to 10 mL 0.1 M sodium citrate buffer (pH 4.8) and 40 mg/mL tetracycline (to prevent growth of bacteria) in a 50 mL tube in duplicate. The amount of sample added to each tube is listed in Table 50. Some samples were difficult to mix (P132, P132-10, P132-100), so were added at a lower concentration. A positive control of 0.2 grams SolkaFloc 200 NF Powdered Cellulose (lot # UA158072, International Fiber Corporation) and a negative control (no sample) were also included. Enough reverse osmosis (R^(O)) water to bring the volume to a total of 20 mL was added to the tubes. Both the sodium citrate buffer and water were heated to 50° C. prior to use.

Accellerase® 1000 enzyme was added to each tube at a dosage of 0.25 mL per gram of biomass (highest dosage recommended by Genencor). The tubes were incubated at 45° angle at 150 rpm and 50 degrees C. (recommended by Genencor) for 72 hours. Samples were taken at 0, 3, 6, 9, 12, 18, 24, 48, and 72 hours (Table 52 and 53), centrifuged at 14,000 rpm for 20 minutes and the supernatant frozen at −20° C. The glucose concentration in the samples was analyzed using the YSI Biochem Analyzer (Interscience) using the conditions described in Table 51. A glucose standard solution of 2.5 g/L was prepared by dissolving 2.500 grams glucose (Sigma Cat# G7528-5KG, Lot#: 107H0245) in distilled water. Once dissolved, the total volume was brought to 1 L with distilled water in a volumetric flask. The standard was prepared fresh weekly and stored at 4° C.

TABLE 50 Amount of Each Sample Added Amount added to Tube Xyleco Number (g/20 mL) P132 0.5 P132-10 0.5 P132-100 0.5 A132 0.75 A132-10 0.75 A132-100 0.75 G132 0.75 G132-10 0.75 G132-100 0.75 WS132 0.75 WS132-10 0.75 WS132-100 0.75 Sample A 0.75 SolkaFloc 200NF 0.2 (Control) Negative Control 0

TABLE 51 YSI Components Used in Shake Flask Study Component Catalog # Lot # YSI Glucose Membrane 2365 07D100124 YSI Glucose Buffer 2357 014614A

Results

TABLE 52 Cellulase Assay Results Glucose Concentration (mg/mL) at Incubation Time (hours) Sample Number 0 3 6 9 12 18 24 48 72 P132 0.59 4.19 7.00 8.72 9.70 10.95 12.19 15.10 15.65 P132-10 0.36 3.37 5.08 6.39 6.98 7.51 8.99 11.25 11.65 P132-100 0.91 3.86 5.67 7.31 8.08 9.47 10.70 12.70 13.80 A132 0.39 1.51 1.92 2.40 2.64 3.04 3.30 3.90 4.06 A132-10 0.42 1.80 2.27 2.63 2.86 3.16 3.43 4.02 4.14 A132-100 0.46 2.09 2.72 3.16 3.43 3.78 4.09 4.84 5.26 G132 0.40 1.16 1.35 1.52 1.60 1.67 1.85 2.10 2.21 G132-10 0.34 1.34 1.64 1.95 2.03 2.09 2.36 2.77 3.02 G132-100 0.61 1.84 2.32 2.89 3.14 3.52 3.97 4.81 5.44 WS132 0.35 1.48 1.81 2.14 2.26 2.50 2.70 3.18 3.26 WS132-10 0.44 1.77 2.22 2.60 2.76 2.61 3.15 3.62 3.82 WS132-100 0.70 2.76 3.63 4.59 4.78 5.29 5.96 6.99 7.43 Sample A 0.42 1.09 1.34 1.55 1.69 1.66 2.17 2.96 3.71 Negative Control (no 0.03 0.03 0.01 0.01 0.02 0.01 0.02 0.02 0.02 sample) Positive Control 0.17 2.38 3.65 4.71 5.25 5.98 7.19 9.26 9.86 (SolkaFloc)

Plots of Glucose Concentration (g/L) vs. Time (hours) for the Top Four Producers in Table 52 are shown in FIG. 39.

The amount of cellulose digested in the tube was calculated as follows:

g/mL glucose×20 mL (volume of sample)×0.9 (to correct for the water molecule added upon hydrolysis of cellulose)

The percent of the total sample released as glucose (in Table 53 below) was calculated as follows:

g of cellulose digested/g of sample added (see Table 5 for details)*100

TABLE 53 Cellulase Assay Results Percent of the Total Sample Released as Glucose (%) at Incubation Time (h) Sample Number 0 3 6 9 12 18 24 48 72 P132 2.02 14.98 25.16 31.36 34.85 39.38 43.81 54.29 56.27 P132-10 1.19 12.02 18.25 22.97 25.06 27.00 32.29 40.43 41.87 P132-100 3.17 13.79 20.38 26.28 29.02 34.06 38.45 45.65 49.61 A132 0.86 3.55 4.58 5.74 6.29 7.27 7.87 9.31 9.70 A132-10 0.94 4.25 5.42 6.29 6.82 7.56 8.18 9.60 9.89 A132-100 1.03 4.94 6.50 7.56 8.18 9.05 9.77 11.57 12.58 G132 0.89 2.71 3.22 3.62 3.79 3.98 4.39 4.99 5.26 G132-10 0.74 3.14 3.91 4.66 4.82 4.99 5.62 6.60 7.20 G132-100 1.39 4.34 5.54 6.91 7.49 8.42 9.48 11.50 13.01 WS132 0.77 3.48 4.32 5.11 5.38 5.98 6.43 7.58 7.78 WS132-10 0.98 4.18 5.30 6.22 6.58 6.24 7.51 8.64 9.12 WS132-100 1.61 6.55 8.69 10.99 11.42 12.67 14.26 16.73 17.78 Sample A 0.94 2.54 3.19 3.70 4.01 3.96 5.16 7.06 8.86 Positive 1.29 21.15 32.72 42.30 47.07 53.73 64.53 83.16 88.56 Control (SolkaFloc)

Example 30 Shake Flask Fermentation Using Pichia stipitis Summary

Shake flask fermentation using Pichia stipitis was performed using four cellulosic materials having the highest % performance from Table 36.

Protocol

Experiments were run under the parameters outlined in Tables 54-56.

TABLE 54 Equipment and Frequency of Maintenance Frequency of Equipment Manufacturer, Name Maintenance Shakers (2) B. Braun Biotech, Quarterly Certomat BS-1 Spectrophotometer Unicam, UV300 Biannual YSI Biochem Analyzer Interscience, YSI Monthly

TABLE 55 YSI Components Used in Shake Flask Study Component Reference # Lot # YSI Ethanol Membrane 2786 07M100361 YSI Ethanol Standard (3.2 2790 1271040 g/L) YSI Ethanol Buffer 2787 07J100215

TABLE 56 Chemicals Used for Shake Flask Fermentation Media Component Manufacturer Reference # Lot # Urea ScholAR 9472706 AD-7284-43 Chemistry Yeast Nitrogen Becton Dickinson 291940 7128171 Base Peptone Becton Dickinson 211677 4303198 YM Broth Becton Dickinson 271120 6278265 Xylose Alfa Aesar A10643 10130919 Glucose Fisher Scientific BP350-1 030064

Seed Development

For all the following shake flask experiments the seed flasks were prepared using the following procedure.

A working cell bank of P. stipitis NRRL Y-7124 was prepared from a rehydrated lyophilized culture obtained from ARS Culture Collection. Cryovials containing P. stipitis culture in 15% v/v glycerol were stored at −75° C. A portion of the thawed working cell bank material was streaked onto a Yeast Mold (YM) Broth+20 g/L agar (pH 5.0) and incubated at 30° C. for 2 days. The plates were held for 2 days at 4° C. before use. A 250 mL Erlenmeyer flask containing 100 mL of medium (40 g/L glucose, 1.7 g/L yeast nitrogen base, 2.27 g/L urea, 6.56 g/L peptone, 40 g/L xylose, pH 5.0) was inoculated with one colony and incubated for 24 hours at 25° C. and 100 rpm. After 23 hours of growth, a sample was taken and analyzed for optical density (600 nm in a UV spectrophotometer) and purity (Gram stain). Based on these results, one flask (called the Seed Flask) at an optical density of between 4 and 8 and with a clean Gram stain was used to inoculate all of the test flasks.

Three experiments were run using samples A132-10, A132-100, G132-10, and G132-100. Experiment #1 tested these four samples for ethanol concentration at varying concentrations of xylose and at constant concentrations of glucose. Experiment #2 tested these four samples for ethanol concentration at double the concentration of feedstock used in the experiments of Table 36. Finally, experiment #3 tested these four samples for ethanol concentration while varying both the xylose and the glucose concentrations, simultaneously.

Experiment #1—Varying the Xylose Concentration

Four cellulosic samples (A132-10, A132-100, G132-10, and G132-100) were tested at varying xylose concentrations as listed in Table 57 below.

TABLE 57 Media Composition of Experiment #1 Flasks Xylose Glucose Concentration Concentration Treatment (g/L) (g/L) 100% Xylose  40.0 40.0 50% Xylose 20.0 40.0 25% Xylose 10.0 40.0 10% Xylose 4.0 40.0  0% Xylose 0.0 40.0

The test vessels (a total of 40, 250 mL Erlenmeyer flasks) contained 100 mL of medium. Five different types of media were prepared with the amount of xylose and glucose outlined in Table 57. In addition, the media contained 1.7 g/L yeast nitrogen base (Becton Dickinson # 291940) 2.27 g/L urea (ScholAR Chemistry #9472706), and 6.56 g/L peptone (Becton Dickinson #211677). All flasks were autoclaved empty at 121° C. and 15 psi and filter sterilized (0.22 μm filter) media was added to the flasks prior to the addition of the test materials. Flasks were held at room temperature for 4 days and inspected for contamination (cloudiness) prior to use. The test materials were not sterilized, as autoclaving will change the content of the samples and filter sterilization not appropriate for sterilization of solids. The test samples (A132-10, A132-100, G132-10, and G132-100 at 5 g per 100 mL) were added at the time of inoculation (rather than prior to) to reduce the possibility of contamination. In addition to the test samples, 1 mL (1% v/v) of seed flask material was added to each flask. The flasks were incubated at 30° C. and 150 rpm for 72 hours.

Unfortunately, one flask (sample A132-100 with 100% Xylose) was broken during the testing. Therefore, all results past 24 hours of incubation are reported as a single flask. After 72 hours of incubation, 100% of the original amount of cellulosic material (5.0 g) was added to the 100% Xylose flasks (7 flasks in total, one flask containing sample A132-100 was broken) and incubated as above for an additional 48 hours.

TABLE 58 Addition of Feedstock to 100% Xylose Flasks at Incubation Time 72 hours Added at Feedstock 72 hours (grams) A132-10 5 A132-100 5 G132-10 5 G132-100 5

Analysis

Samples were taken from the 40 test flasks at incubation times of 0, 6, 12, 24, 36, 48, and 72 hours. In addition, samples were taken at 24 and 48 hours post-addition of the second feedstock amount in the 100% Xylose flasks (see Table 58).

A total of 292 samples were analyzed for ethanol concentration using a YSI Biochem Analyzer based on the alcohol dehydrogenase assay (YSI, Interscience). Samples were centrifuged at 14,000 rpm for 20 minutes and the supernatant stored at −20° C. Of note, time 0 samples required filtration through a 0.45 μm syringe filter. The samples will be diluted to between 0-3.2 g/L ethanol prior to analysis. A standard of 2.0 g/L ethanol was analyzed approximately every 30 samples to ensure the integrity of the membrane was maintained.

A total of 47 samples were analyzed for cell count. Samples will be taken at 72 hours incubation and 48 hours post-addition of more cellulosic material. Appropriately diluted samples were mixed with 0.05% Trypan blue and loaded into a Neubauer haemocytometer. The cells were counted under 40× magnification.

Experiment #2—Analysis of 2× Feedstock Concentration

The test vessels (a total of 8, 250 mL Erlenmeyer flasks) contained 100 mL of medium. The media contained 40 g/L glucose, 40 g/L xylose, 1.7 g/L yeast nitrogen base (Becton Dickinson # 291940) 2.27 g/L urea (ScholAR Chemistry #9472706), and 6.56 g/L peptone (Becton Dickinson #211677). Flasks were prepared as in Experiment #1. The test samples (A132-10, A132-100, G132-10, and G132-100 at 10 g per 100 mL) were added at the time of inoculation (rather than prior to) to reduce the possibility of contamination. In addition to the test samples, 1 mL (1% v/v) of seed flask material was added to each flask. The flasks were incubated at 30° C. and 150 rpm above for 72 hours.

Analysis

Samples were from the 8 test flasks at an incubation time of 0, 6, 12, 24, 36, 48, and 72 hours. Ethanol analys3s of the 56 samples were performed as per experiment #1 and are reported in Table 59. A cell count was performed on the 72 hour sample as per experiment #1 and is presented in Table 60.

TABLE 59 Ethanol Concentration in Flasks with Double Feedstock Sample Ethanol Concentration (g/L) Time A132-10 A132-100 G132-10 G132-100 0 1.38 0.26 0.12 0.11 6 1.75 0.21 0.20 0.10 12 2.16 0.73 0.69 0.31 24 19.05 15.35 16.55 12.60 36 21.75 17.55 18.00 15.30 48 26.35 23.95 24.65 20.65 72 26.95 27.35 28.90 27.40

TABLE 60 Cell Concentration at 72 hour Incubation Time in Flasks with Double Feedstock Cell Concentration Sample (×10⁸/mL) A132-10 4.06 A132-100 5.37 G132-10 5.18 G132-100 4.47

Experiment #3—Varying Xylose and Glucose Concentrations

Four cellulosic samples (A132-10, A132-100, G132-10, and G132-100) were tested at varying xylose and glucose concentrations as listed in the table below (Table 60).

TABLE 61 Media Composition of Experiment #3 Flasks Xylose Glucose Concentration Concentration Treatment (g/L) (g/L) 50% Sugar 20.0 20.0 25% Sugar 10.0 10.0 10% Sugar 4.0 4.0  0% Sugar 0.0 0

The test vessels (a total of 32, 250 mL Erlenmeyer flasks) contained 100 mL of medium. Four different types of media were prepared with the amount of xylose and glucose outlined in Table 61. In addition, the media contained 1.7 g/L yeast nitrogen base (Becton Dickinson # 291940) 2.27 g/L urea (ScholAR Chemistry #9472706), and 6.56 g/L peptone (Becton Dickinson #211677). The flasks were prepared as per Experiment #1. The test samples (A132-10, A132-100, G132-10, and G132-100) were added at the time of inoculation (rather than prior to) to reduce the possibility of contamination. In addition to the test samples, 1 mL (1% v/v) of seed flask material was added to each flask. The flasks were incubated at 30° C. and 150 rpm for 72 hours.

Analysis

Samples were taken from the 32 test flasks at an incubation time of 0, 6, 12, 24, 36, 48, and 72 hours (see Tables 62-65). A total of 224 samples were analyzed for ethanol concentration using the YSI Biochem Analyzer based on the alcohol dehydrogenase assay (YSI, Interscience). Samples were centrifuged at 14,000 rpm for 20 minutes and the supernatant stored at −20° C. Of note, some of the samples required centrifugation and then filtration through a 0.45 μm syringe filter. The samples were diluted to between 0-3.2 g/L ethanol prior to analysis. A standard of 2.0 g/L ethanol was analyzed approximately every 30 samples to ensure the integrity of the YSI membrane was maintained.

TABLE 62 Ethanol Results Sample A132-10 Ethanol Concentration (g/L) Sample 0% 10% 25% 50% 100% 0% 10% 25% 50% Time Xylose Xylose Xylose Xylose Xylose Sugars* Sugars* Sugars* Sugars*  0 0.43 0.42 0.42 0.41 0.39 0.53 0.57 0.56 0.56  6 1.16 1.16 1.15 1.16 1.12 0.93 0.91 0.83 0.88 12 1.72 1.86 1.71 1.79 1.90 1.21 2.13 2.47 2.32 24 15.55 15.90 17.05 17.05 16.95 1.02 4.88 9.77 13.35 36 17.10 17.40 20.25 21.35 20.25 1.29 4.27 9.99 17.55 48 16.40 17.05 19.70 23.00 26.80 1.47 3.03 8.33 16.60 72 15.15 15.55 19.25 21.85 28.00 1.14 1.52 5.08 14.20 24 — — — — 23.15 — — — — hours post- addition 48 — — — — 21.55 — — — — hours post- addition *Analysis from experiment #3.

TABLE 63 Ethanol Results Sample A132-100 Ethanol Concentration (g/L) Sample 0% 10% 25% 50% 100% 0% 10% 25% 50% Time Xylose Xylose Xylose Xylose Xylose Sugars* Sugars* Sugars* Sugars*  0 0.11 0.09 0.17 0.20 0.18 0.12 0.14 0.09 0.13  6 0.13 0.15 0.15 0.15 0.14 0.10 0.11 0.11 0.13 12 0.88 1.00 1.18 1.25 0.89 0.18 1.58 1.55 1.57 24 15.90 15.70 16.50 16.05 14.60** 0.18 3.33 7.99 11.15 36 16.00 17.90 16.90 19.45 17.80** 0.21 2.85 8.37 16.10 48 15.75 16.70 19.30 22.15 27.00** 0.54 1.47 7.54 15.60 72 14.85 15.35 18.55 21.30 28.50** 0.78 0.51 4.47 12.90 24 — — — — 24.80** — — — — hours post- addition 48 — — — — 23.60** — — — — hours post- addition *Analysis from experiment #3. **All results based on analysis of one flask.

TABLE 64 Ethanol Results Sample G132-10 Ethanol Concentration (g/L) Sample 0% 10% 25% 50% 100% 0% 10% 25% 50% Time Xylose Xylose Xylose Xylose Xylose Sugars* Sugars* Sugars* Sugars*  0 0.09 0.08 0.08 0.08 0.08 0.05 0.05 0.05 0.06  6 0.14 0.13 0.14 0.14 0.13 0.11 0.12 0.11 0.12 12 1.01 0.96 1.00 0.87 1.14 0.48 1.60 1.79 1.71 24 15.90 15.70 16.30 16.05 14.60 0.13 3.96 8.54 11.10 36 15.10 17.45 16.80 18.75 22.15 0.09 3.02 8.69 16.55 48 15.95 16.90 19.25 21.10 24.00 0.07 2.05 8.10 16.50 72 13.50 15.80 18.55 21.25 26.55 0.09 0.11 5.55 14.15 24 — — — — 24.95 — — — — hours post- addition 48 — — — — 24.20 — — — — hours post- addition *Analysis from experiment #3.

TABLE 65 Ethanol Results Sample G132-100 Ethanol Concentration (g/L) 10% 25% 50% 0% w/v w/v w/v 100% w/v 0% 10% 25% 50% Sample Time Xylose Xylose Xylose Xylose Xylose Sugars* Sugars* Sugars* Sugars*  0 0.04 0.04 0.04 0.04 0.05 0.05 0.05 0.05 0.06  6 0.07 0.07 0.08 0.08 0.07 0.04 0.05 0.05 0.06 12 0.60 0.56 0.67 0.58 0.71 0.13 1.37 1.48 1.44 24 13.05 14.45 14.90 13.95 12.05 0.03 3.67 7.62 10.55 36 15.10 17.10 18.25 18.20 19.25 0.01 3.09 8.73 16.10 48 14.40 17.00 19.35 22.55 24.45 0.01 1.91 7.76 15.85 72 14.70 15.40 18.45 22.10 27.55 0.03 0.01 5.08 14.30 24 hours — — — — 25.20 — — — — post- addition 48 hours — — — — 24.60 — — — — post- addition *Analysis from experiment #3.

Samples were taken at 72 hours incubation for cell counts (see Tables 66-67). Appropriately diluted samples were mixed with 0.05% Trypan blue and loaded into a Neubauer haemocytometer. The cells were counted under 40× magnification.

Results

One seed flask was used to inoculate all Experiment #1 and #2 test flasks. The optical density (600 nm) of the seed flask was measured to be 5.14 and the cell concentration was 4.65×10⁸ cells/mL (Tables 65-66). Therefore, the initial concentration of cells in the test flasks was approximately 4.65×10⁶ cells/mL.

A second seed flask was used to inoculate Experiment #3 flasks. The optical density (600 nm) of the seed flask was 5.78 and the cell concentration was 3.75×10⁸ cells/mL. Therefore, the initial concentration of cells in the test flasks was approximately 3.75×10⁶ cells/mL.

TABLE 66 Cell Counts at Incubation Time of 72 hours Cell Concentration (× 10⁸/mL) 0% 10% 25% 50% 100% 0% 10% 25% 50% Sample Xylose Xylose Xylose Xylose Xylose Sugar Sugar Sugar Sugar A132-10 0.37 0.63 3.72 4.92 4.05 0.26 0.22 0.26 1.54 A132-100 0.99 1.07 0.99 0.78 1.97 0.03* 0.33 0.44 1.81 G132-10 0.95 4.50 2.67 2.67 3.82 0.01* 0.17 0.49 1.92 G132-100 6.53 4.02 4.84 4.47 5.29 0.01* 0.33 0.89 2.22 *Samples were heavily contaminated after 72 hours of growth. This is expected because the Pichia did not grow well without sugar added, and contaminants (from the non-sterile samples) were able to out-grow the Pichia.

TABLE 67 Cell Counts at Incubation Time of 48 hours Post-Addition (100% Xylose and Glucose) Cell Concentration Sample (×10⁸/mL) A132-10 10.17 A132-100 3.38 G132-10 3.94 G132-100 6.53

Example 31 Toxicity Testing of Lignocellulosic Samples against P. stipitis and S. cerevisiae Summary

Thirty-seven samples were analyzed for toxicity against two ethanol-producing cultures, Saccharomyces cerevesiae and Pichia stipitis. In this study, glucose was added to the samples in order to distinguish between starvation of the cultures and toxicity of the samples.

TABLE 68 Conditions for Toxicity Testing Organism Saccharomyces Pichia cerevisiae stipitis Variable ATCC 24858 NRRL Y-7124 Inoculation Volume (mL) 0.5-1 1 (target 6-7 × 10⁵ (target 3-4 × 10⁶ cells/mL) cells/mL) Test Repetition Single Flasks Incubation Temperature 25° C. 25° C. (±1° C.) Shaker Speed (rpm) 200 125 Type of Container 500 mL 250 mL Erlenmeyer Flask Erlenmeyer Flask Media volume 100 mL 100 mL Total Incubation time  72  72 (hours) Ethanol Analysis 0, 6, 12, 24, 36, 48, 72 0, 6, 12, 24, 36, 48, 72 (hours) Cell Counts (hours) 24, 72 24, 72 pH 0 hours 0 hours

Protocol

A summary of the protocol used is listed in Table 68. A description of the chemicals used in toxicity testing is listed in Table 69. Two control flasks (no sample added) were performed for each microorganism for each week of testing. A total of 82 flasks were analyzed.

During the experiments, no ethanol or cells appeared in the P. stipitis flasks containing samples C, C-1e, C-5e, and C-10e in the first 24 hours of incubation. In order to confirm the results, the test was repeated. The second test confirmed some inhibition of P. stipitis growth when samples C, C1E, C5E, and C10E were added to the flasks.

TABLE 69 Chemicals and Materials Used for Toxicity Testing Media Component Manufacturer Reference # Lot # Urea ScholAR Chemistry 9472706 AD-7284-43 Yeast Nitrogen Becton Dickinson 291940 7128171 Base Peptone Becton Dickinson 211677 4303198 Xylose Alfa Aesar A10643 10130919 Glucose Sigma G-5400 107H0245 Yeast Extract Becton Dickinson 288620 4026828 YM Broth Becton Dickinson 271120 6278265

TABLE 70 YSI Components Used in Toxicity Study Component Catalogue # YSI Ethanol Membrane 2786 YSI Ethanol Standard (3.2 g/L) 2790 YSI Ethanol Buffer 2787

Test Samples

Seven test samples (all with the C designation) were ground using a coffee grinder suitable for small samples. The samples were ground to a consistent particle size (between samples) with the naked eye. Sample number C-100e ground easily to a small particle size.

All samples were added to the flasks at a concentration of 50 grams per liter with the exception of the six P samples (25 grams per liter). These samples were white to off-white in color and visually fluffy and the flasks would not mix properly (not enough free liquid) at the 50 grams per liter concentration. Samples S dissolved easily and could in the future be added to the flasks at a higher concentration. Samples A and G could be added at 100 grams per liter in the future.

Testing was performed using the two microorganisms as described below.

Saccharomyces cerevisiae ATCC 24858 (American Type Culture Collection)

A working cell bank of S. cerevisiae ATCC 24858 was prepared from a rehydrated lyophilized culture obtained from American Type Culture Collection. Cryovials containing S. cerevisiae culture in 15% v/v glycerol are stored at −75° C. A portion of the thawed working cell bank material will be streaked onto a Yeast Mold (YM) Broth+20 g/L agar (pH 5.0) and incubated at 30° C. for 2 days. A 250 mL Erlenmeyer flask containing 50 mL of medium (20 g/L glucose, 3 g/L yeast extract, and 5.0 g/L peptone, pH 5.0) was inoculated with one colony from the YM plate and incubated for 24 hours at 25° C. and 200 rpm. After 23 hours of growth, a sample was taken and analyzed for optical density (600 nm in a UV spectrophotometer) and purity (Gram stain). Based on these results, one flask (called the Seed Flask) with an OD of 9-15 and pure Gram stain was to be used for inoculating the growth flasks. After 23 hours of growth, the seed flask had a low OD (5.14) and cell count (1.35×10⁸ cells/mL). Of note, the colony taken from the seed plate was smaller than usual. Therefore, 0.5 mL of seed material (as opposed to the planned 0.1 mL) was added to each test vessel.

The test vessels were 500 mL Erlenmeyer flasks containing 100 mL of the sterile medium described above. All flasks were autoclaved at 121° C. and 15 psi prior to the addition of the test materials. The test materials were not sterilized, as autoclaving would change the content of the samples. The test samples were added at the time of inoculation (rather than prior to) to reduce the possibility of contamination. In addition to the test samples, 0.5-1.0 mL (0.5-1.0% v/v) of seed flask material was added to each flask. The flasks were incubated as described above for 72 hours.

Pichia stipitis (ARS Culture Collection)

A working cell bank of P. stipitis NRRL Y-7124 was prepared from a rehydrated lyophilized culture obtained from ARS Culture Collection. Cryovials containing P. stipitis culture in 15% v/v glycerol are stored at −75° C. A portion of the thawed working cell bank material was streaked onto a Yeast Mold (YM) Broth+20 g/L agar (pH 5.0) and incubated at 30° C. for 2 days. The plates were held for up to 5 days at 4° C. before use. A 250 mL Erlenmeyer flask containing 100 mL of medium (40 g/L glucose, 1.7 g/L yeast nitrogen base, 2.27 g/L urea, 6.56 g/L peptone, 40 g/L xylose, pH 5.0) was inoculated with one colony and incubated for 24 hours at 25° C. and 125 rpm. After 23 hours of growth, a sample was taken and analyzed for optical density (600 nm in a UV spectrophotometer) and purity (Gram stain). Based on these results, one flask (called the Seed Flask) at an optical density of 5-9 and with a pure Gram Stain was used to inoculate all of the test flasks.

The test vessels were 250 mL Erlenmeyer flasks containing 100 mL of the sterile medium described above. All flasks were autoclaved empty at 121° C. and 15 psi and filter sterilized (0.22 μm filter) medium added to the flasks prior to the addition of the test materials. The test materials were not sterilized, as autoclaving would change the content of the samples and filter sterilization not appropriate for sterilization of solids. The test samples were added at the time of inoculation (rather than prior to) to reduce the possibility of contamination. In addition to the test samples, 1 mL (1% v/v) of seed flask material was added to each flask. The flasks were incubated as described above for 72 hours.

Analysis

Samples were taken from seed flasks just prior to inoculation and each test flask at 24 and 72 hours and analyzed for cell concentration using direct counts. Appropriately diluted samples of S. cerevisiae and P. stipitis were mixed with 0.05% Trypan blue, loaded into a Neubauer haemocytometer. The cells were counted under 40× magnification.

Samples were taken from each flask at 0, 6, 12, 24, 36, 48 and 72 hours and analyzed for ethanol concentration using the YSI Biochem Analyzer based on the alcohol dehydrogenase assay (YSI, Interscience). Samples were centrifuged at 14,000 rpm for 20 minutes and the supernatant stored at −20° C. The samples will be diluted to 0-3.2 g/L ethanol prior to analysis. A standard of 2.0 g/L ethanol was analyzed approximately every 30 samples to ensure the integrity of the membrane was maintained during analysis.

Calculations

The following calculations were used to compare the cell counts and ethanol concentration to the control flasks.

% performance=(concentration of ethanol in test flask/ethanol in control)*100% cells=(number of cells in test flask/number of cells in control flask)*100

Results

The S. cerevisiae seed flask had an optical density (600 nm) of 5.14 and a cell concentration of 1.35×10⁸ cells/mL. One half mL of seed flask material was added to each of the test flasks. Therefore, the starting cell concentration in each flask was 6.75×10⁵/mL. During the second week of testing, the S. cerevisiae seed flask had an optical density (600 nm) of 4.87 and a cell concentration of 3.15×10⁷ cells/mL. One mL of seed flask material was added to each of the test flasks. Therefore, the starting cell concentration in each flask was 6.30×10⁵/mL. The pH of the S. cerevisiae flasks at a sample time of 0 hours is presented in Table 71. The pH of the flask contents was within the optimal pH for S. cerevisiae growth (pH 4-6). No pH adjustment was required.

TABLE 71 pH of S. cerevisiae flasks at sample time 0 hours Sample Sample Number pH Number pH P 5.04 C 5.46 P1E 4.99 C1E 5.54 P5E 5.04 C5E 5.50 P10E 4.98 C10E 5.33 P50E 4.67 C30E 5.12 P100E 4.43 C50E 4.90 G 5.45 C100E 4.66 G1E 5.47 ST 5.11 G5E 5.46 ST1E 5.06 G10E 5.39 ST5E 4.96 G50E 5.07 ST10E 4.94 A 5.72 ST30E 5.68 A1E 5.69 ST50E 4.48 A5E 5.62 ST100E 4.23 A10E 5.61 control A 5.02 A50E 5.74 control B 5.04 S* 5.10 S1E 5.08 S5E 5.07 S10E 5.04 S30E 4.84 S50E 4.57 S100E 4.33 *“S” refers to sucrose *“C” refers to corn *“ST” refers to starch

The ethanol concentration and performance in the S. cerevisiae flasks are presented in Table 72 and 73. The highest ethanol concentrations were produced by the S series.

TABLE 72 Ethanol Concentration in S. cerevisiae flasks Ethanol Concentration (g/L) at the Sample following times (hours) Number 0 6 12 24 36 48 72 P 0.02 0.04 0.38 5.87 7.86 5.41 1.04 P1E 0.03 0.03 0.28 5.10 8.03 5.46 0.58 P5E 0.03 0.04 0.57 8.84 6.38 3.40 0.04 P10E 0.06 0.05 0.65 6.63 7.66 5.57 1.40 P50E 0.04 0.03 0.26 2.80 5.85 8.59 5.68 P100E 0.04 0.02 0.12 3.64 8.26 7.51 3.03 G 0.04 0.04 0.57 10.20 8.24 6.66 2.84 G1E 0.04 0.05 0.46 10.20 9.24 6.94 2.84 G5E 0.11 0.11 0.44 10.00 8.7 6.36 0.88 G10E 0.05 0.04 0.40 9.97 8.41 5.79 0.11 G50E 0.05 0.05 0.48 9.72 8.33 6.13 2.38 A 0.29 0.38 0.48 8.43 8.76 7.09 4.66 A1E 0.34 0.44 0.79 9.66 8.9 7.18 2.64 A5E 0.55 0.45 0.99 9.44 8.96 7.56 3.80 A10E 0.55 0.55 0.93 9.58 8.33 6.28 1.40 A50E 0.22 0.08 0.38 9.38 8.01 5.99 0.98 S 0.03 0.03 0.39 5.73 7.06 10.10 15.90 S1E 0.05 0.06 0.31 7.24 9.52 12.10 14.90 S5E 0.02 0.05 0.34 5.87 7.68 11.90 19.00 S10E 0.03 0.04 0.35 5.88 7.72 11.50 19.30 S30E 0.03 0.05 0.09 5.94 7.97 11.20 20.40 S50E* 0.13 0.19 0.47 5.46 7.96 13.00 18.30 S100E 0.11 0.10 0.21 7.00 10.6 13.80 12.70 C 0.01 0.04 0.32 8.47 7.57 5.48 6.40 C1E 0.00 0.06 0.37 8.93 7.86 5.99 1.37 C5E 0.03 0.05 0.48 9.32 7.92 5.69 1.41 C10E 0.02 0.04 0.52 9.14 7.67 5.34 0.35 C30E 0.02 0.05 0.28 9.15 8.15 5.84 2.47 C50E 0.03 0.06 0.44 9.31 7.79 5.78 1.79 C100E 0.03 0.06 0.58 9.06 6.85 5.95 1.09 ST 0.02 0.05 0.99 8.54 6.69 5.09 0.42 ST1E 0.03 0.04 0.70 8.87 7.29 4.81 1.04 ST5E 0.02 0.04 0.52 8.61 7.16 4.97 0.85 ST10E 0.02 0.05 0.33 8.97 7.05 5.26 0.68 ST30E 0.03 0.04 0.71 8.47 6.96 4.89 0.21 ST50E 0.04 0.07 0.34 8.46 8.19 7.04 3.20 ST100E 0.03 0.10 0.30 9.30 8.62 7.29 4.23 control A 0.01 0.07 0.85 5.92 8.18 7.81 6.26 control B 0.01 0.04 0.27 4.86 6.43 8.01 6.75 control A* 0.04 0.21 1.36 5.19 7.31 7.55 5.16 control B* 0.03 0.20 1.18 5.16 5.96 7.62 5.32 *analyzed week 2 See Table 72 for Sample Number key

TABLE 73 Performance in S. cerevisiae flasks Performance (%) at Sample the following times (hours) Number 24 36 48 72 P 108.9 107.6 68.4 16.0 P1E 94.6 109.9 69.0 8.9 P5E 164.0 87.3 43.0 0.6 P10E 123.0 104.9 70.4 21.5 P50E 51.9 80.1 108.6 87.3 P100E 67.5 113.1 94.9 46.5 G 189.2 112.8 84.2 43.6 G1E 189.2 126.5 87.7 43.6 G5E 185.5 119.1 80.4 13.5 G10E 185.0 115.1 73.2 1.7 G50E 180.3 114.0 77.5 36.6 A 156.4 119.9 89.6 71.6 A1E 179.2 121.8 90.8 40.6 A5E 175.1 122.7 95.6 58.4 A10E 177.7 114.0 79.4 21.5 A50E 174.0 109.7 75.7 15.1 S 106.3 96.6 127.7 244.2 S1E 134.3 130.3 153.0 228.9 S5E 108.9 105.1 150.4 291.9 S10E 109.1 105.7 145.4 296.5 S30E 110.2 109.1 141.6 313.4 S50E* 105.5 119.9 171.3 349.2 S100E 129.9 145.1 174.5 195.1 C 157.1 103.6 69.3 98.3 C1E 165.7 107.6 75.7 21.0 C5E 172.9 108.4 71.9 21.7 C10E 169.6 105.0 67.5 5.4 C30E 169.8 111.6 73.8 37.9 C50E 172.7 106.6 73.1 27.5 C100E 168.1 93.8 75.2 16.7 ST 158.4 91.6 64.3 6.5 ST1E 164.6 99.8 60.8 16.0 ST5E 159.7 98.0 62.8 13.1 ST10E 166.4 96.5 66.5 10.4 ST30E 157.1 95.3 61.8 3.2 ST50E 157.0 112.1 89.0 49.2 ST100E 172.5 118.0 92.2 65.0 control A 109.8 112.0 98.7 96.2 control B 90.2 88.0 101.3 103.7 control A* 100.3 110.1 99.5 98.5 control B* 99.7 89.8 100.4 101.5 *analyzed week 2

The cell concentration and % cells in the S. cerevisiae flasks are presented in Table 74. High cell counts were observed in all flasks; however, not all of the cells appear to be making ethanol.

TABLE 74 S cerevisiae Cell Counts and % Cells Cell Count % Cells (count/ Sample (cells × 10⁸/mL) count control) * 100 Number 24 hours 72 hours 24 hours 72 hours P 0.62 0.96 97.7 139.0 P1E 0.35 1.18 54.1 170.9 P5E 1.13 1.93 177.3 279.5 P10E 0.59 1.42 91.8 205.6 P50E 0.32 1.40 49.4 202.8 P100E 0.45 1.94 70.6 281.0 G 0.74 3.48 116.5 504.0 G1E 0.68 3.65 107.1 528.6 G5E 0.62 3.87 96.5 560.5 G10E 0.70 2.73 109.5 395.4 G50E 0.46 2.10 71.8 304.1 A 0.55 3.53 86.0 511.2 A1E 0.83 3.45 130.7 499.6 A5E 0.67 3.53 104.8 511.2 A10E 0.53 1.95 83.6 282.4 A50E 0.66 1.62 103.5 234.6 S 0.44 1.11 69.5 160.8 S1E 0.44 1.10 68.2 159.3 S5E 0.23 0.99 36.5 143.4 S10E 0.39 0.73 61.2 105.4 S30E 0.31 0.71 48.3 102.1 S50E* 0.44 0.90 86.5 196.5 S100E 0.53 0.84 82.4 121.7 C 0.45 1.81 70.6 262.1 C1E 0.71 2.40 110.6 347.6 C5E 0.53 2.33 83.6 337.4 C10E 0.77 1.55 120.0 224.5 C30E 0.75 1.80 117.6 260.7 C50E 0.64 1.70 100.1 246.2 C100E 0.81 1.51 127.1 218.7 ST 0.75 1.75 117.6 253.4 ST1E 0.57 1.36 89.4 197.0 ST5E 0.58 1.49 90.7 215.8 ST10E 0.61 1.32 95.4 191.2 ST30E 0.59 0.60 91.8 86.9 ST50E 0.59 1.30 91.8 188.3 ST100E 0.41 1.24 63.5 179.6 control A 0.81 0.79 127.1 114.1 control B 0.47 0.59 72.9 85.9 control A* 0.66 0.42 131.2 91.7 control B* 0.35 0.50 69.0 108.1

The P. stipitis seed flask had an optical density (600 nm) of 5.01 and a cell concentration of 3.30×10⁸ cells/mL. One mL of seed flask material was added to each of the test flasks. Therefore, the starting cell concentration in each flask was 3.30×10⁶/mL. During the second week of testing, the P. stipitis seed flask had an optical density (600 nm) of 5.45 and a cell concentration of 3.83×10⁸ cells/mL. One mL of seed flask material was added to each of the test flasks. Therefore, the starting cell concentration in each flask was 3.83×10⁶/mL. The pH of the P. stipitis flasks at a sample time of 0 hours is presented in Table 75. The pH of the flask contents was within the optimal pH for P. stipitis growth (pH 4-7). No pH adjustment was required.

TABLE 75 pH of P. stipitis Flasks at Sample Time 0 Hours Sample Sample Number pH Number pH P 4.91 C 5.36 P1E 4.87 C1E 5.30 P5E 4.90 C5E 5.29 P10E 4.78 C10E 5.06 P50E 4.46 C30E 4.89 P100E 4.24 C50E 4.70 G 5.45 C100E 4.59 G1E 5.43 ST 4.93 G5E 5.48 ST1E 4.90 G10E 5.32 ST5E 4.81 G50E 4.99 ST10E 4.83 A 5.69 ST30E 4.91 A1E 5.66 ST50E 4.24 A5E 5.60 ST100E 4.07 A10E 5.58 control A 4.93 A50E 5.69 control B 4.91 S 5.00 S1E 4.94 S5E 4.86 S10E 4.78 S30E 4.51 S50E 4.27 S100E 4.08

The ethanol concentration and performance in the P. stipitis flasks are presented in Table 76 and 77. The highest ethanol concentrations were the G and A series. Flasks C-30e, C-50e, and C-100e also contained high concentrations of ethanol. The cell concentration and % cells in the P. stipitis flasks are presented in Table 78. Low cell concentrations were observed in the flasks with the S designations. Low cell counts were also observed in flasks containing samples C, C1E, C5E, and C10E at the 24 hour sample time.

TABLE 76 Ethanol concentration in P. stipitis flasks Ethanol Concentration (g/L) at the Sample following times (hours) Number 0 6 12 24 36 48 72 P 0.01 0.05 0.26 4.98 8.57 14.10 17.00 P1E 0.02 0.03 0.04 4.24 9.03 12.40 17.30 P5E 0.02 0.03 0.42 6.72 12.40 15.60 18.60 P10E 0.02 0.02 0.01 1.38 8.69 13.00 17.00 P50E 0.01 0.02 0.02 0.03 3.77 10.50 16.90 P100E 0.02 0.03 0.02 3.75 10.50 15.60 18.80 G 0.02 0.08 0.20 10.80 17.70 19.40 25.40 G1E 0.04 0.12 0.50 12.20 19.60 23.80 28.60 G5E 0.07 0.14 0.73 12.50 19.10 24.50 27.50 G10E 0.04 0.19 0.42 10.20 19.10 22.90 28.20 G50E 0.05 0.22 0.25 8.73 18.40 22.20 28.00 A 0.13 0.28 0.82 16.10 19.40 19.30 18.60 A1E 0.22 0.59 1.08 16.10 22.40 27.60 27.70 A5E 0.32 0.43 0.43 10.60 22.10 27.10 28.10 A10E 0.33 0.61 1.15 14.90 22.00 27.10 27.90 A50E 0.30 0.10 0.47 13.40 20.20 24.80 27.10 S 0.01 0.01 0.26 3.68 7.50 10.20 13.30 S1E 0.02 0.02 0.22 4.98 9.22 11.60 14.20 S5E 0.02 0.02 0.19 4.25 8.50 11.70 14.70 S10E 0.03 0.02 0.17 2.98 8.87 11.90 14.70 S30E 0.08 0.05 0.03 2.96 8.73 12.60 16.50 S50E 0.08 0.05 0.04 2.24 6.13 7.95 12.50 S100E 0.11 0.10 0.08 3.36 7.82 10.50 13.90 C* 0.02 0.03 0.05 0.23 1.66 2.68 6.57 C1E* 0.03 0.03 0.03 0.07 0.95 1.85 10.20 C5E* 0.03 0.02 0.04 0.05 0.37 1.59 4.80 C10E* 0.03 0.04 0.04 0.05 3.91 15.20 28.30 C30E 0.01 0.03 0.60 12.30 21.20 26.00 27.20 C50E 0.02 0.02 0.45 12.30 19.50 23.80 29.20 C100E 0.05 0.04 0.38 11.40 18.70 22.90 27.70 ST 0.03 0.03 0.37 6.69 10.70 13.50 10.90 ST1E 0.01 0.00 0.48 5.24 9.37 12.50 15.70 ST5E 0.02 0.03 0.29 5.45 10.10 11.90 14.70 ST10E 0.02 0.02 0.42 5.60 9.44 12.20 14.90 ST30E 0.05 0.04 0.73 5.70 9.50 12.10 15.20 ST50E 0.02 0.05 0.19 5.16 9.47 12.70 15.20 ST100E* 0.07 0.15 0.11 4.98 10.70 15.40 18.80 control A 0.02 0.03 0.37 4.05 7.50 9.24 11.50 control B 0.02 0.02 0.30 4.22 7.44 9.44 11.50 control A* 0.02 0.05 0.69 4.86 8.69 11.10 16.40 control B* 0.02 0.05 0.74 5.96 10.80 13.00 14.00 *analyzed week 2

TABLE 77 Performance in P. stipitis flasks Performance (%) at Sample the following times (hours) Number 24 36 48 72 P 120.3 114.7 151.0 147.8 P1E 102.4 120.9 132.8 150.4 P5E 162.3 166.0 167.0 161.7 P10E 33.3 116.3 139.2 147.8 P50E 0.7 50.5 112.4 147.0 P100E 90.6 140.6 167.0 163.5 G 260.9 236.9 207.7 220.9 G1E 294.7 262.4 254.8 248.7 G5E 301.9 255.7 262.3 239.1 G10E 246.4 255.7 245.2 245.2 G50E 210.9 246.3 237.7 243.5 A 388.9 259.7 206.6 161.7 A1E 388.9 299.9 295.5 240.9 A5E 256.0 295.9 290.1 244.3 A10E 359.9 294.5 290.1 242.6 A50E 323.7 270.4 265.5 235.7 S 88.9 100.4 109.2 115.7 S1E 120.3 123.4 124.2 123.5 S5E 102.7 113.8 125.3 127.8 S10E 72.0 118.7 127.4 127.8 S30E 71.5 116.9 134.9 143.5 S50E 54.1 82.1 85.1 108.7 S100E 81.2 104.7 112.4 120.9 C* 4.2 17.0 22.2 43.2 C1E* 1.4 9.7 15.4 67.1 C5E* 0.9 3.8 13.2 31.6 C10E* 0.9 40.1 126.1 246.1 C30E 297.1 283.8 278.4 236.5 C50E 297.1 261.0 254.8 253.9 C100E 275.4 250.3 245.2 240.9 ST 161.6 143.2 144.5 94.8 ST1E 126.6 125.4 133.8 136.5 ST5E 131.6 135.2 127.4 127.8 ST10E 135.3 126.4 130.6 129.6 ST30E 137.7 127.2 129.6 132.2 ST50E 124.6 126.8 136.0 132.2 ST100E* 120.3 109.7 127.8 123.7 control A 97.8 100.4 98.9 100.0 control B 101.9 99.6 101.1 100.0 control A* 89.8 89.1 92.1 107.9 control B* 110.2 110.8 107.9 92.1 *analyzed in week 2

TABLE 78 P. stipitis Cell Counts and % Cells Cell Count % Cells (count/ Sample (cells × 10⁸/mL) count control) * 100 Number 24 hours 72 hours 24 hours 72 hours P 2.78 11.00 80.6 148.0 P1E 2.10 7.20 60.9 96.9 P5E 2.93 9.68 84.9 130.3 P10E 1.42 7.73 41.2 104.0 P50E 0.33 8.63 9.6 116.2 P100E 1.58 8.25 45.8 111.0 G 1.50 14.20 43.5 191.1 G1E 3.90 8.10 113.0 109.0 G5E 2.93 6.45 84.9 86.8 G10E 4.35 13.30 126.1 179.0 G50E 3.75 11.60 108.7 156.1 A 7.43 8.55 215.4 115.1 A1E 4.13 9.53 119.7 128.3 A5E 3.68 9.75 106.7 131.2 A10E 4.50 7.50 130.4 100.9 A50E 6.23 5.33 180.6 71.7 S 3.53 5.55 102.3 74.7 S1E 3.00 3.30 87.0 44.4 S5E 3.68 3.00 106.7 40.4 S10E 1.73 5.78 50.1 77.8 S30E 2.55 5.48 73.9 73.8 S50E 2.63 6.15 76.2 82.8 S100E 2.25 4.43 65.2 59.6 C* 0.00 0.26 0.00 7.2 C1E* 0.00 0.36 0.00 9.9 C5E* 0.00 0.08 0.00 2.1 C10E* 0.00 5.85 0.00 160.7 C30E 5.78 4.20 167.5 56.5 C50E 3.40 7.35 98.6 98.9 C100E 1.98 6.60 57.4 88.8 ST 2.55 7.65 73.9 103.0 ST1E 2.00 8.70 58.0 117.1 ST5E 1.85 6.75 53.6 90.8 ST10E 1.83 5.40 53.0 72.7 ST30E 2.78 6.15 80.6 82.8 ST50E 1.33 3.45 38.6 46.4 ST100E* 4.35 3.83 59.8 105.2 control A 3.60 7.13 104.3 96.0 control B 3.30 7.73 95.7 104.0 control A* 7.50 3.23 103.0 88.7 control B* 7.05 4.05 96.8 111.3 *analyzed week 2

Cell Toxicity Results Summary Zymomonas Mobilis

As shown in FIG. 40A, elevated cell numbers (e.g., greater than the control) were observed in samples containing P-132-10, G-132-10, and WS-132-10 at the 24 hour time point. Cell numbers in the presence of all other samples were comparable to the control. This observation indicates that the substrates were not toxic towards Z. mobilis for up to 24 hours after seeding.

At the 36 hour time point, a decrease in cell numbers (e.g., due to a loss of cells or cell death) was observed for all samples, including the control. The greatest decrease in cell numbers was observed for those samples containing P-132-10, G-132-10. The likely cause of this effect is common to all samples, including the control. Thus, the cause of this effect is not the test substrates, as these vary in each sample, and are not present in the control. Possible explanations for this observation include inappropriate culture conditions (e.g., temperature, media compositions), or ethanol concentrations in the sample.

As shown in FIG. 40B, all cells produced comparable amounts of ethanol (e.g., 5-10 g/L) at each time point, irrespective of the substrate. Consistent with the cell number data presented in FIG. 40A, ethanol concentration in each sample peaked at the 24 hour time point. In contrast to the cell number data, ethanol concentration did not decrease at subsequent time points. This was expected as ethanol was not removed from the system. In addition, this data suggests that ethanol production in these samples may have resulted from fermentation of glucose in the culture media. None of the substrates tested appeared to increase ethanol production.

Together, FIGS. 40A and 40B suggest that ethanol concentrations above about 6 g/L may be toxic to Z. mobilis. This data is also presented as a percentage normalized against the control, as shown in FIG. 40C.

Pichia stipitis

As shown in Chart 2A FIG. 41A, cell numbers were comparable to the control. Furthermore, although slightly reduced cell numbers were present in samples containing G-132 and WS-132, reduced cell numbers were not observed for G-132-10, G-132-100, A-132-10, or A-132-100. Thus, it is unlikely that substrates G or A are toxic. Rather, the reduced cell numbers observed for G-132 and WS-132 are likely to have been caused by an experimental anomaly or by the presence of unprocessed substrate somehow impeding cell growth. Overall, this data suggests that glucose present in the control and experimental samples is likely to be sufficient to promote optimal P. stipitis growth, and that the presence of an additional substrate in the sample does not increase this growth rate. These results also suggest that none of the samples are toxic in P. stipitis.

As shown in FIG. 41B, despite the similar cell numbers reported in FIG. 41B, greatly increased ethanol production was observed in all samples containing an experimental substrate. Ethanol concentrations increased over time for each of the three time points tested. The highest concentration of ethanol was observed for A-132-10 at the 48 hour time point (e.g., approximately 26.0 g/L). By comparing the substrate concentrations with the highest levels of ethanol production with the cell number data presented in FIG. 41B, it can be seen that P. stipitis do not appear to be sensitive to increasing ethanol concentrations. Furthermore, ethanol production does not appear to be related to cell number, but rather appears to be related to the type of substrate present in the sample.

Together, the results presented in FIGS. 41A and 41B suggest that the experimental substrates do not promote increased P. stipitis growth, however, they greatly increase the amount of ethanol produced by this cell type. This data is also presented as a percentage normalized against the control, as shown in FIG. 41C.

Saccharomyces cerevisiae

As shown in FIG. 42A, G-132-100, A-132, A-132-10, A-132-100, and WS-132 promoted slightly elevated cell numbers compared to the control. No significant reductions in cell number were observed for any sample. These results suggest that none of the samples are toxic in S. cerevisiae.

As shown in FIG. 42B, increased ethanol production was observed in cells treated with each cell type compared to the control. Comparison of those samples containing the highest amount of ethanol with the cell number data presented in FIG. 42A suggests that ethanol concentrations in excess of 5 g/L may have had an adverse effect on cell numbers. However, this observation is not the case for all samples.

This data is also presented as a percentage normalized against the control, as shown in FIG. 42C.

In conclusion, none of the samples tested appeared to be toxic in Z. mobilis, P. stipitis, or S. cerevisiae. Furthermore, P. stipitis appeared to be the most efficient of the three cell types for producing ethanol from the experimental substrates tested.

Example 32 Alcohol Production Using Irradiation-Sonication Pretreatment

The optimum size for biomass conversion plants is affected by factors including economies of scale and the type and availability of biomass used as feedstock. Increasing plant size tends to increase economies of scale associated with plant processes. However, increasing plant size also tends to increase the costs (e.g., transportation costs) per unit of biomass feedstock. Studies analyzing these factors suggest that the appropriate size for biomass conversion plants can range from 2000 to 10,000 dried tons of biomass feedstock per day. The plant described below is sized to process 2000 tons of dry biomass feedstock per day.

FIG. 43 shows a process schematic of a biomass conversion system configured to process switchgrass. The feed preparation subsystem processes raw biomass feedstock to remove foreign objects and provide consistently sized particles for further processing. The pretreatment subsystem changes the molecular structure (e.g., reduces the average molecular weight and the crystallinity) of the biomass feedstock by irradiating the biomass feedstock, mixing the irradiated the biomass feedstock with water to form a slurry, and applying ultrasonic energy to the slurry. The irradiation and sonication convert the cellulosic and lignocellulosic components of the biomass feedstock into fermentable materials. The primary process subsystem ferments the glucose and other low weight sugars present after pretreatment to form alcohols.

Feed Preparation

The selected design feed rate for the plant is 2,000 dry tons per day of switchgrass biomass. The design feed is chopped and/or sheared switchgrass.

Biomass feedstock, in the form of bales of switchgrass, is received by the plant on truck trailers. As the trucks are received, they are weighed and unloaded by forklifts. Some bales are sent to on-site storage while others are taken directly to the conveyors. From there, the bales are conveyed to an automatic unwrapping system that cuts away the plastic wrapping and/or net surrounding the bales. The biomass feedstock is then conveyed past a magnetic separator to remove tramp metal, after which it is introduced to shredder-shearer trains where the material is reduced in size. Finally, the biomass feedstock is conveyed to the pretreatment subsystem.

In some cases, the switchgrass bales are wrapped with plastic net to ensure they don't break apart when handled, and may also be wrapped in plastic film to protect the bale from weather. The bales are either square or round. The bales are received at the plant from off-site storage on large truck trailers.

Since switchgrass is only seasonally available, long-term storage is required to provide feed to the plant year-round. Long-term storage will likely consist of 400-500 acres of uncovered piled rows of bales at a location (or multiple locations) reasonably close to the ethanol plant. On-site short-term storage is provided equivalent to 72 hours of production at an outside storage area. Bales and surrounding access ways as well as the transport conveyors will be on a concrete slab. A concrete slab is used because of the volume of traffic required to deliver the large amount of biomass feedstock required. A concrete slab will minimize the amount of standing water in the storage area, as well as reduce the biomass feedstock's exposure to dirt. The stored material provides a short-term supply for weekends, holidays, and when normal direct delivery of material into the process is interrupted.

The bales are off-loaded by forklifts and are placed directly onto bale transport conveyors or in the short-term storage area. Bales are also reclaimed from short-term storage by forklifts and loaded onto the bale transport conveyors.

Bales travel to one of two bale unwrapping stations. Unwrapped bales are broken up using a spreader bar and then discharged onto a conveyor, which passes a magnetic separator to remove metal prior to shredding. A tramp iron magnet is provided to catch stray magnetic metal and a scalping screen removes gross oversize and foreign material ahead of multiple shredder-shearer trains, which reduce the biomass feedstock to the proper size for pretreatment. The shredder-shearer trains include shredders and rotary knife cutters. The shredders reduce the size of the raw biomass feedstock and feed the resulting material to the rotary knife cutters. The rotary knife cutters concurrently shear the biomass feedstock and screen the resulting material.

Three storage silos are provided to limit overall system downtime due to required maintenance on and/or breakdowns of feed preparation subsystem equipment. Each silo can hold approximately 55,000 cubic feet of biomass feedstock (˜3 hours of plant operation).

Pretreatment

A conveyor belt carries the biomass feedstock from the feed preparation subsystem 110 to the pretreatment subsystem 114. As shown in FIG. 44, in the pretreatment subsystem 114, the biomass feedstock is irradiated using electron beam emitters, mixed with water to form a slurry, and subjected to the application of ultrasonic energy. As discussed above, irradiation of the biomass feedstock changes the molecular structure (e.g., reduces the average molecular weight and the crystallinity) of the biomass feedstock. Mixing the irradiated biomass feedstock into a slurry and applying ultrasonic energy to the slurry further changes the molecular structure of the biomass feedstock. Application of the radiation and sonication in sequence may have synergistic effects in that the combination of techniques appears to achieve greater changes to the molecular structure (e.g., reduces the average molecular weight and the crystallinity) than either technique can efficiently achieve on its own. Without wishing to be bound by theory, in addition to reducing the polymerization of the biomass feedstock by breaking intramolecular bonds between segments of cellulosic and lignocellulosic components of the biomass feedstock, the irradiation may make the overall physical structure of the biomass feedstock more brittle. After the brittle biomass feedstock is mixed into a slurry, the application of ultrasonic energy further changes the molecular structure (e.g., reduces the average molecular weight and the crystallinity) and also can reduce the size of biomass feedstock particles.

Electron Beam Irradiation

The conveyor belt 491 carrying the biomass feedstock into the pretreatment subsystem distributes the biomass feedstock into multiple feed streams (e.g., 50 feed streams) each leading to separate electron beam emitters 492. In this embodiment, the biomass feedstock is irradiated while it is dry. Each feed stream is carried on a separate conveyor belt to an associated electron beam emitter. Each irradiation feed conveyor belt can be approximately one meter wide. Before reaching the electron beam emitter, a localized vibration is induced in each conveyor belt to evenly distribute the dry biomass feedstock over the cross-sectional width of the conveyor belt.

Electron beam emitter 492 (e.g., electron beam irradiation devices commercially available from Titan Corporation, San Diego, Calif.) are configured to apply a 100 kilo-Gray dose of electrons applied at a power of 300 kW. The electron beam emitters are scanning beam devices with a sweep width of 1 meter to correspond to the width of the conveyor belt. In some embodiments, electron beam emitters with large, fixed beam widths are used. Factors including belt/beam width, desired dose, biomass feedstock density, and power applied govern the number of electron beam emitters required for the plant to process 2,000 tons per day of dry feed.

Sonication

The irradiated biomass feedstock is mixed with water to form a slurry before ultrasonic energy is applied. There can be a separate sonication system associated with each electron beam feed stream or several electron beam streams can be aggregated as feed for a single sonication system.

In each sonication system, the irradiated biomass feedstock is fed into a reservoir 1214 through a first intake 1232 and water is fed into the reservoir 1214 through second intake 1234. Appropriate valves (manual or automated) control the flow of biomass feedstock and the flow of water to produce a desired ratio of biomass feedstock to water (e.g., 10% cellulosic material, weight by volume). Each reservoir 1214 includes a mixer 1240 to agitate the contents of volume 1236 and disperse biomass feedstock throughout the water.

In each sonication system, the slurry is pumped (e.g., using a recessed impeller vortex pump 1218) from reservoir 1214 to and through a flow cell 1224 including an ultrasonic transducer 1226. In some embodiments, pump 1218 is configured to agitate the slurry 1216 such that the mixture of biomass feedstock and water is substantially uniform at inlet 1220 of the flow cell 1224. For example, the pump 1218 can agitate the slurry 1216 to create a turbulent flow that persists throughout the piping between the first pump and inlet 1220 of flow cell 1224.

Within the flow cell 1224, ultrasonic transducer 1226 transmits ultrasonic energy into slurry 1216 as the slurry flows through flow cell 1224. Ultrasonic transducer 1226 converts electrical energy into high frequency mechanical energy (e.g., ultrasonic energy), which is then delivered to the slurry through booster 48. Ultrasonic transducers are commercially available (e.g., from Hielscher USA, Inc. of Ringwood, N.J.) that are capable of delivering a continuous power of 16 kilowatts.

The ultrasonic energy traveling through booster 1248 in reactor volume 1244 creates a series of compressions and rarefactions in process stream 1216 with an intensity sufficient to create cavitation in process stream 1216. Cavitation disaggregates components of the biomass feedstock including, for example, cellulosic and lignocellulosic material dispersed in process stream 1216 (e.g., slurry). Cavitation also produces free radicals in the water of process stream 1216 (e.g., slurry). These free radicals act to further break down the cellulosic material in process stream 1216. In general, about 250 MJ/m³ of ultrasonic energy is applied to process stream 1216 containing fragments of poplar chips. Other levels of ultrasonic energy (between about 5 and about 4000 MJ/m³, e.g., 10, 25, 50, 100, 250, 500, 750, 1000, 2000, or 3000) can be applied to other biomass feedstocks After exposure to ultrasonic energy in reactor volume 1244, process stream 1216 exits flow cell 24 through outlet 1222.

Flow cell 1224 also includes a heat exchanger 1246 in thermal communication with at least a portion of reactor volume 1244. Cooling fluid 1248 (e.g., water) flows into heat exchanger 1246 and absorbs heat generated when process stream 1216 (e.g., slurry) is sonicated in reactor volume 1244. In some embodiments, the flow of cooling fluid 1248 into heat exchanger 1246 is controlled to maintain an approximately constant temperature in reactor volume 1244. In addition or in the alternative, the temperature of cooling fluid 1248 flowing into heat exchanger 1246 is controlled to maintain an approximately constant temperature in reactor volume 1244.

The outlet 1242 of flow cell 1224 is arranged near the bottom of reservoir 1214 to induce a gravity feed of process stream 1216 (e.g., slurry) out of reservoir 1214 towards the inlet of a second pump 1230 which pumps process stream 1216 (e.g., slurry) towards the primary process subsystem.

Sonication systems can include a single flow path (as described above) or multiple parallel flow paths each with an associated individual sonication unit. Multiple sonication units can also be arranged to series to increase the amount of sonic energy applied to the slurry.

Primary Processes

A vacuum rotary drum type filter removes solids from the slurry before fermentation. Liquid from the filter is pumped cooled prior to entering the fermentors. Filtered solids are passed to the post-processing subsystem for further processing.

The fermentation tanks are large, low pressure, stainless steel vessels with conical bottoms and slow speed agitators. Multiple first stage fermentation tanks can be arranged in series. The temperature in the first stage fermentation tanks is controlled to 30 degrees centigrade using external heat exchangers. Yeast is added to the first stage fermentation tank at the head of each series of tanks and carries through to the other tanks in the series.

Second stage fermentation consists of two continuous fermentors in series. Both fermentors are continuously agitated with slow speed mechanical mixers. Temperature is controlled with chilled water in external exchangers with continuous recirculation. Recirculation pumps are of the progressive cavity type because of the high solids concentration.

Off gas from the fermentation tanks and fermentors is combined and washed in a counter-current water column before being vented to the atmosphere. The off gas is washed to recover ethanol rather than for air emissions control.

Post-Processing Distillation

Distillation and molecular sieve adsorption are used to recover ethanol from the raw fermentation beer and produce 99.5% ethanol. Distillation is accomplished in two columns—the first, called the beer column, removes the dissolved CO₂ and most of the water, and the second concentrates the ethanol to a near azeotropic composition.

All the water from the nearly azeotropic mixture is removed by vapor phase molecular sieve adsorption. Regeneration of the adsorption columns requires that an ethanol water mixture be recycled to distillation for recovery.

Fermentation vents (containing mostly CO2, but also some ethanol) as well as the beer column vent are scrubbed in a water scrubber, recovering nearly all of the ethanol. The scrubber effluent is fed to the first distillation column along with the fermentation beer.

The bottoms from the first distillation contain all the unconverted insoluble and dissolved solids. The insoluble solids are dewatered by a pressure filter and sent to a combustor. The liquid from the pressure filter that is not recycled is concentrated in a multiple effect evaporator using waste heat from the distillation. The concentrated syrup from the evaporator is mixed with the solids being sent to the combustor, and the evaporated condensate is used as relatively clean recycle water to the process.

Because the amount of stillage water that can be recycled is limited, an evaporator is included in the process. The total amount of the water from the pressure filter that is directly recycled is set at 25%. Organic salts like ammonium acetate or lactate, steep liquor components not utilized by the organism, or inorganic compounds in the biomass end up in this stream. Recycling too much of this material can result in levels of ionic strength and osmotic pressures that can be detrimental to the fermenting organism's efficiency. For the water that is not recycled, the evaporator concentrates the dissolved solids into a syrup that can be sent to the combustor, minimizing the load to wastewater treatment.

Wastewater Treatment

The wastewater treatment section treats process water for reuse to reduce plant makeup water requirements. Wastewater is initially screened to remove large particles, which are collected in a hopper and sent to a landfill. Screening is followed by anaerobic digestion and aerobic digestion to digest organic matter in the stream. Anaerobic digestion produces a biogas stream that is rich in methane that is fed to the combustor. Aerobic digestion produces a relatively clean water stream for reuse in the process as well as a sludge that is primarily composed of cell mass. The sludge is also burned in the combustor. This screening/anaerobic digestion/aerobic digestion scheme is standard within the current ethanol industry and facilities in the 1-5 million gallons per day range can be obtained as “off-the-shelf” units from vendors.

Combustor Boiler and Turbo-Generator

The purpose of the combustor, boiler, and turbo-generator subsystem is to burn various by-product streams for steam and electricity generation. For example, some lignin, cellulose, and hemicellulose remains unconverted through the pretreatment and primary processes. The majority of wastewater from the process is concentrated to a syrup high in soluble solids. Anaerobic digestion of the remaining wastewater produces a biogas high in methane. Aerobic digestion produces a small amount of waste biomass (sludge). Burning these by-product streams to generate steam and electricity allows the plant to be self sufficient in energy, reduces solid waste disposal costs, and generates additional revenue through sales of excess electricity.

Three primary fuel streams (post-distillate solids, biogas, and evaporator syrup) are fed to a circulating fluidized bed combustor. The small amount of waste biomass (sludge) from wastewater treatment is also sent to the combustor. A fan moves air into the combustion chamber. Treated water enters the heat exchanger circuit in the combustor and is evaporated and superheated to 510° C. (950° F.) and 86 atm (1265 psia) steam. Flue gas from the combustor preheats the entering combustion air then enters a baghouse to remove particulates, which are landfilled. The gas is exhausted through a stack.

A multistage turbine and generator are used to generate electricity. Steam is extracted from the turbine at three different conditions for injection into the pretreatment reactor and heat exchange in distillation and evaporation. The remaining steam is condensed with cooling water and returned to the boiler feedwater system along with condensate from the various heat exchangers in the process. Treated well water is used as makeup to replace steam used in direct injection.

Other Embodiments

A number of embodiments of the invention have been described. Nevertheless, it will be understood that various modifications may be made without departing from the spirit and scope of the invention.

In some embodiments, relatively low doses of radiation, optionally, combined with acoustic energy, e.g., ultrasound, are utilized to crosslink, graft, or otherwise increase the molecular weight of a natural or synthetic carbohydrate-containing material, such as any of those materials in any form (e.g., fibrous form) described herein, e.g., sheared or un-sheared cellulosic or lignocellulosic materials, such as cellulose. The cross-linking, grafting, or otherwise increasing the molecular weight of the natural or synthetic carbohydrate-containing material can be performed in a controlled and predetermined manner by selecting the type or types of radiation employed (e.g., e-beam and ultraviolet or e-beam and gamma) and/or dose or number of doses of radiation applied. Such a material having increased molecular weight can be useful in making a composite, such as a fiber-resin composite, having improved mechanical properties, such as abrasion resistance, compression strength, fracture resistance, impact strength, bending strength, tensile modulus, flexural modulus and elongation at break. Cross-linking, grafting, or otherwise increasing the molecular weight of a selected material can improve the thermal stability of the material relative to an un-treated material. Increasing the thermal stability of the selected material can allow it to be processed at higher temperatures without degradation. In addition, treating materials with radiation can sterilize the materials, which can reduce their tendency to rot, e.g., while in a composite. The cross-linking, grafting, or otherwise increasing the molecular weight of a natural or synthetic carbohydrate-containing material can be performed in a controlled and predetermined manner for a particular application to provide optimal properties, such as strength, by selecting the type or types of radiation employed and/or dose or doses of radiation applied.

When used, the combination of radiation, e.g., low dose radiation, and acoustic energy, e.g., sonic or ultrasonic energy, can improve material throughput and/or minimize energy usage.

The resin can be any thermoplastic, thermoset, elastomer, adhesive, or mixtures of these resins. Suitable resins include any resin, or mixture of resins described herein.

In addition to the resin alone, the material having the increased molecular weight can be combined, blended, or added to other materials, such as metals, metal alloys, ceramics (e.g., cement), lignin, organic or inorganic additives, elastomers, asphalts, glass, or mixtures of any of these and/or resins. When added to cement, fiber-reinforced cements can be produced having improved mechanical properties, such as the properties described herein, e.g., compression strength and/or fracture resistance.

Cross-linking, grafting, or otherwise increasing the molecular weight of a natural or synthetic carbohydrate-containing material utilizing radiation can provide useful materials in many forms and for many applications. For example, the carbohydrate-containing material can be in the form of a paper product, such as paper, paper pulp, or paper effluent, particle board, glued lumber laminates, e.g., veneer, or plywood, lumber, e.g., pine, poplar, oak, or even balsa wood lumber. Treating paper, particle board, laminates or lumber, can increase their mechanical properties, such as their strength. For example, treating pine lumber with radiation can make a high strength structural material.

When paper is made using radiation, radiation can be utilized at any point in its manufacture. For example, the pulp can be irradiated, a pressed fiber preform can be irradiated, or the finished paper itself can be irradiated. In some embodiments, radiation is applied at more than one point during the manufacturing process.

For example, a fibrous material that includes a first cellulosic and/or lignocellulosic material having a first molecular weight can be irradiated in a manner to provide a second cellulosic and/or lignocellulosic material having a second molecular weight higher than the first molecular weight. For example, if gamma radiation is utilized as the radiation source, a dose of from about 0.2 Mrad to about 10 Mrad, e.g., from about 0.5 Mrad to about 7.5 Mrad, or from about 2.0 Mrad to about 5.0 Mrad, can be applied. If e-beam radiation is utilized, a smaller dose can be utilized (relative to gamma radiation), such as a dose of from about 0.1 Mrad to about 5 Mrad, e.g., between about 0.2 Mrad to about 3 Mrad, or between about 0.25 Mrad and about 2.5 Mrad. After the relatively low dose of radiation, the second cellulosic and/or lignocellulosic material can be combined with a material, such as a resin, and formed into a composite, e.g., by compression molding, injection molding or extrusion. Forming resin-fiber composites is described in WO 2006/102543. Once composites are formed, they can be irradiated to further increase the molecular weight of the carbohydrate-containing material while in the composite.

Alternatively, a fibrous material that includes a first cellulosic and/or lignocellulosic material having a first molecular weight can be combined with a material, such as a resin, to provide a composite, and then the composite can be irradiated with a relatively low dose of radiation so as to provide a second cellulosic and/or lignocellulosic material having a second molecular weight higher than the first molecular weight. For example, if gamma radiation is utilized as the radiation source, a dose of from about 1 Mrad to about 10 Mrad can be applied. Using this approach increases the molecular weight of the material while it is with a matrix, such as a resin matrix. In some embodiments, the resin is a cross-linkable resin, and, as such, it crosslinks as the carbohydrate-containing material increases in molecular weight, which can provide a synergistic effect to provide maximum mechanical properties to a composite. For example, such composites can have excellent low temperature performance, e.g., having a reduced tendency to break and/or crack at low temperatures, e.g., temperatures below 0° C., e.g., below −10° C., −20° C., −40° C., −50° C., −60° C. or even below −100° C., and/or excellent performance at high temperatures, e.g., capable of maintaining their advantageous mechanical properties at relatively high temperature, e.g., at temperatures above 100° C., e.g., above 125° C., 150° C., 200° C., 250° C., 300° C., 400° C., or even above 500° C. In addition, such composites can have excellent chemical resistance, e.g., resistance to swelling in a solvent, e.g., a hydrocarbon solvent, resistance to chemical attack, e.g., by strong acids, strong bases, strong oxidants (e.g., chlorine or bleach) or reducing agents (e.g., active metals such as sodium and potassium).

In some embodiments, the resin, or other matrix material, does not crosslink during irradiation. In some embodiments, additional radiation is applied while the carbohydrate-containing material is within the matrix to further increase the molecular weight of the carbohydrate-containing material. In some embodiments, the radiation causes bonds to form between the matrix and the carbohydrate-containing material.

In some embodiments, the carbohydrate-containing material is in the form of fibers. In such embodiments, when the fibers are utilized in a composite, the fibers can be randomly oriented within the matrix. In other embodiments, the fibers can be substantially oriented, such as in one, two, three or four directions. If desired, the fibers can be continuous or discrete.

Any of the following additives can be added to the fibrous materials, densified fibrous materials, or any other materials and composites described herein. Additives, e.g., in the form of a solid, a liquid or a gas, can be added, e.g., to the combination of a fibrous material and resin. Additives include fillers such as calcium carbonate, graphite, wollastonite, mica, glass, fiber glass, silica, and talc; inorganic flame retardants such as alumina trihydrate or magnesium hydroxide; organic flame retardants such as chlorinated or brominated organic compounds; ground construction waste; ground tire rubber; carbon fibers; or metal fibers or powders (e.g., aluminum, stainless steel). These additives can reinforce, extend, or change electrical, mechanical or compatibility properties. Other additives include lignin, fragrances, coupling agents, compatibilizers, e.g., maleated polypropylene, processing aids, lubricants, e.g., fluorinated polyethylene, plasticizers, antioxidants, opacifiers, heat stabilizers, colorants, foaming agents, impact modifiers, polymers, e.g., degradable polymers, photostabilizers, biocides, antistatic agents, e.g., stearates or ethoxylated fatty acid amines. Suitable antistatic compounds include conductive carbon blacks, carbon fibers, metal fillers, cationic compounds, e.g., quaternary ammonium compounds, e.g., N-(3-chloro-2-hydroxypropyl)-trimethylammonium chloride, alkanolamides, and amines. Representative degradable polymers include polyhydroxy acids, e.g., polylactides, polyglycolides and copolymers of lactic acid and glycolic acid, poly(hydroxybutyric acid), poly(hydroxyvaleric acid), poly[lactide-co-(e-caprolactone)], poly[glycolide-co-(e-caprolactone)], polycarbonates, poly(amino acids), poly(hydroxyalkanoate)s, polyanhydrides, polyorthoesters and blends of these polymers.

When described additives are included, they can be present in amounts, calculated on a dry weight basis, of from below 1 percent to as high as 80 percent, based on total weight of the fibrous material. More typically, amounts range from between about 0.5 percent to about 50 percent by weight, e.g., 5 percent, 10 percent, 20 percent, 30, percent or more, e.g., 40 percent.

Any additives described herein can be encapsulated, e.g., spray dried or microencapsulated, e.g., to protect the additives from heat or moisture during handling.

The fibrous materials, densified fibrous materials, resins or additives may be dyed. For example, the fibrous material can be dyed before combining with the resin and compounding to form composites. In some embodiments, this dyeing can be helpful in masking or hiding the fibrous material, especially large agglomerations of the fibrous material, in molded or extruded parts, when this is desired. Such large agglomerations, when present in relatively high concentrations, can show up as speckles in the surfaces of the molded or extruded parts.

For example, the desired fibrous material can be dyed using an acid dye, direct dye or a reactive dye. Such dyes are available from Spectra Dyes, Kearny, N.J. or Keystone Aniline Corporation, Chicago, Ill. Specific examples of dyes include SPECTRA™ LIGHT YELLOW 2G, SPECTRACID™ YELLOW 4GL CONC 200, SPECTRANYL™ RHODAMINE 8, SPECTRANYL™ NEUTRAL RED B, SPECTRAMINE™ BENZOPERPURINE, SPECTRADIAZO™ BLACK OB, SPECTRAMINE™ TURQUOISE G, and SPECTRAMINE™ GREY LVL 200%, each being available from Spectra Dyes.

In some embodiments, resin color concentrates containing pigments are blended with dyes. When such blends are then compounded with the desired fibrous material, the fibrous material may be dyed in-situ during the compounding. Color concentrates are available from Clariant.

It can be advantageous to add a scent or fragrance to the fibrous materials, densified fibrous or composites. For example, it can be advantageous for the composites smell and/or look like natural wood, e.g., cedar wood. For example, the fragrance, e.g., natural wood fragrance, can be compounded into the resin used to make the composite. In some implementations, the fragrance is compounded directly into the resin as an oil. For example, the oil can be compounded into the resin using a roll mill, e.g., a Banbury® mixer or an extruder e.g., a twin-screw extruder with counter-rotating screws. An example of a Banbury® mixer is the F-Series Banbury® mixer, manufactured by Farrel. An example of a twin-screw extruder is the WP ZSK 50 MEGAcompounder™, manufactured by Krupp Werner & Pfleiderer. After compounding, the scented resin can be added to the fibrous material and extruded or molded. Alternatively, master batches of fragrance-filled resins are available commercially from International Flavors and Fragrances, under the trade name Polylff™ or from the RTP Company. In some embodiments, the amount of fragrance in the composite is between about 0.005% by weight and about 10% by weight, e.g., between about 0.1% and about 5% or 0.25% and about 2.5%.

Other natural wood fragrances include evergreen or redwood. Other fragrances include peppermint, cherry, strawberry, peach, lime, spearmint, cinnamon, anise, basil, bergamot, black pepper, camphor, chamomile, citronella, eucalyptus, pine, fir, geranium, ginger, grapefruit, jasmine, juniperberry, lavender, lemon, mandarin, marjoram, musk, myrhh, orange, patchouli, rose, rosemary, sage, sandalwood, tea tree, thyme, wintergreen, ylang ylang, vanilla, new car or mixtures of these fragrances. In some embodiments, the amount of fragrance in the fibrous material-fragrance combination is between about 0.005% by weight and about 20% by weight, e.g., between about 0.1% and about 5% or 0.25% and about 2.5%.

While fibrous materials have been described, such as cellulosic and lignocellulosic fibrous materials, other fillers may be used for making the composites. For example, inorganic fillers such as calcium carbonate (e.g., precipitated calcium carbonate or natural calcium carbonate), aragonite clay, orthorhombic clays, calcite clay, rhombohedral clays, kaolin, clay, bentonite clay, dicalcium phosphate, tricalcium phosphate, calcium pyrophosphate, insoluble sodium metaphosphate, precipitated calcium carbonate, magnesium orthophosphate, trimagnesium phosphate, hydroxyapatites, synthetic apatites, alumina, silica xerogel, metal aluminosilicate complexes, sodium aluminum silicates, zirconium silicate, silicon dioxide or combinations of the inorganic additives may be used. The fillers can have, e.g., a particle size of greater than 1 micron, e.g., greater than 2 micron, 5 micron, 10 micron, 25 micron or even greater than 35 microns.

Nanometer scale fillers can also be used alone, or in combination with fibrous materials of any size and/or shape. The fillers can be in the form of, e.g., a particle, a plate or a fiber. For example, nanometer sized clays, silicon and carbon nanotubes, and silicon and carbon nanowires can be used. The filler can have a transverse dimension less than 1000 nm, e.g., less than 900 nm, 800 nm, 750 nm, 600 nm, 500 nm, 350 nm, 300 nm, 250 nm, 200 nm, less than 100 nm, or even less than 50 nm.

In some embodiments, the nano-clay is a montmorillonite. Such clays are available from Nanocor, Inc. and Southern Clay products, and have been described in U.S. Pat. Nos. 6,849,680 and 6,737,464. The clays can be surface treated before mixing into, e.g., a resin or a fibrous material. For example, the clay can be surface is treated so that its surface is ionic in nature, e.g., cationic or anionic.

Aggregated or agglomerated nanometer scale fillers, or nanometer scale fillers that are assembled into supramolecular structures, e.g., self-assembled supramolecular structures can also be used. The aggregated or supramolecular fillers can be open or closed in structure, and can have a variety of shapes, e.g., cage, tube or spherical.

Accordingly, other embodiments are within the scope of the following claims. 

1. A method comprising: converting a low molecular weight sugar, in a mixture with a fibrous biomass, a microorganism, and water, to a product.
 2. The method of claim 1 wherein converting comprises allowing the microorganism to convert at least a portion of the low molecular weight sugar to ethanol.
 3. The method of claim 2 wherein the microorganism comprises a yeast.
 4. The method of claim 3 wherein the yeast is selected from the group consisting of S. cerevisiae and P. stipitis.
 5. The method of claim 2 wherein the microorganism comprises a bacterium.
 6. The method of claim 5 wherein the bacterium comprises Zymomonas mobilis.
 7. The method of claim 1 further comprising irradiating the fibrous biomass prior to mixing.
 8. The method of claim 7 wherein irradiating comprises irradiating with ionizing radiation.
 9. The method of claim 7 wherein irradiating is performed using a particle beam.
 10. The method claim 7 wherein irradiating is conducted under conditions selected to reduce the molecular weight of the biomass.
 11. The method of claim 7, wherein the ionizing radiation is applied at a total dosage of at least about 5 Mrad.
 12. The method of claim 1 wherein the fibrous biomass has a bulk density of less than about 0.5 g/cm³ prior to addition to the mixture.
 13. The method of claim 1 further comprising physically preparing the biomass.
 14. The method of claim 13 wherein preparing comprises shearing.
 15. The method of claim 13 wherein preparing comprises reducing the size of the biomass by stone grinding, mechanical ripping or tearing, pin grinding, crushing, or air attrition milling.
 16. The method of claim 1 wherein the biomass comprises a cellulosic or lignocellulosic material.
 17. The method of claim 1 wherein the biomass has a BET surface area of greater than 0.25 m²/g.
 18. The method of claim 1 wherein the biomass has a length to diameter ratio of at least
 5. 19. The method of claim 1 wherein converting comprises fermentation.
 20. The method of claim 1, wherein the biomass is selected from the group consisting of paper, paper products, paper waste, wood, particle board, sawdust, agricultural waste, sewage, silage, grasses, rice hulls, bagasse, cotton, jute, hemp, flax, bamboo, sisal, abaca, straw, corn cobs, corn stover, switchgrass, alfalfa, hay, rice hulls, coconut hair, cotton, seaweed, algae, and mixtures thereof.
 21. The method of claim 1 wherein the biomass has internal fibers, and wherein the biomass feedstock has been sheared to an extent that its internal fibers are substantially exposed.
 22. The method of claim 1 wherein the biomass has a porosity greater than 50%.
 23. The method of claim 1 further comprising subjecting the biomass to enzymatic hydrolysis.
 24. The method of claim 23 further comprising converting the hydrolyzed material to the product.
 25. The method of claim 1 wherein the converting step exhibits a % performance is at least 140%.
 26. The method of claim 25 wherein the converting step exhibits a % performance of at least 170%.
 27. The method of claim 1, wherein the product is utilized to produce another product.
 28. A mixture comprising: a low molecular weight sugar, a biomass material, and a solvent.
 29. The mixture of claim 28 further comprising a microorganism. 